intensified eu(iii)extraction using ionic liquids in...
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1
Intensified Eu(III)extraction using ionic liquids in small channels
Qi Li Panagiota Angeli
Department of Chemical Engineering University College London Torrington Place London WC1E 7JE UK
Corresponding author Tel ++44 (0) 20 7679 3832 Fax ++44 (0)20 7383 2348 Email pangeliuclacuk
Abstract
The extraction of Eu(III) from nitric acid solutions was studied in intensified small scale separation units
using an ionic liquid solution (02M n-octyl(phenyl)-NN-diisobutylcarbamoylmethyphosphine oxide
(CMPO) -12M Tributylphosphate) (TBP)1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])as the extraction phase The investigations were
carried out in channels with 02 mm and 05 mm diameter for phase flowrates that result in plug flow
with the aqueous solution as the dispersed phase The interfacial area in plug flow and the velocity
profiles within the plugs were studied with high speed imaging and bright field micro Particle Image
Velocimetry Distribution and mass transfer coefficients were found to have maximum values at nitric
acid concentration of 1M Mass transfer coefficients were higher in the small channel where
recirculation within the plugs and interfacial area are large compared to the large channel for the same
mixture velocities and phase flow rates Within the same channel mass transfer coefficients decreased
with increasing residence time indicating that significant mass transfer takes place at the channel inlet
where the two phases come into contact The experimental results were compared with previous
correlations on mass transfer coefficients in plug flows
1 Introduction
Within the frame of process intensification the miniaturization of chemical operations opens up new
possibilities in separations Microchemical systems with well-defined channel structures in the range of
a few hundred μm are characterised by thin fluid layers and large surface-to-volume ratios which
improve heat and mass transfer rates and coupled with narrow residence time distributions result in
better process efficiency and control (Loumlwe and Ehrfeld 1999 Kiwi-Minsker and Renken 2005) The
increased importance of interfacial phenomena large interfacial areas and the ability to influence flow
patterns make two-phase flows in small units particularly appealing The benefits of microchannel
operation have been clearly demonstrated for liquid-liquid extractions which often involve organic
solvents with high hazard ratings (Kashid et al 2005 Dessimoz et al 2008 Kashid et al 2010
2
Assmann et al 2013 Xu et al 2013 Yang et al 2013)As extraction efficiencies depend on
concentration gradients interfacial area and residence times (Okubo et al 2008) the exact flow pattern
within the separation unit becomes important Plug (or segmented) flow in particular where one phase
forms dispersed plugs with diameter larger than the channel size separated by continuous phase slugs is a
preferred pattern because the circulation patterns forming in the two phases and the thin films separating
the plugs from the channel wall enhance mass transfer (Burns and Ramshaw 2001 Kashid et al 2005
Okubo et al 2008 Jovanović et al 2012) In addition the dispersed plug sizes are very regular and can
be controlled via the choice of the inlet geometry which further reduces non-uniformities common in
large scale extraction units such as mixers-settlers(Khakpay et al 2009) Knowledge of the interfacial
area is very important in the understanding and modelling of extraction operations Chemical reactions
eg alkaline hydrolysis of esters have been used to obtain global values of interfacial area in units such
as agitated contactors(Fernandes and Sharma 1967) packed columns(Puranik and Sharma 1970 Verma
and Sharma 1975)and two-impinging-stream reactors(Dehkordi 2002)In small channels where flow
patterns are well defined high speed imaging can be used to acquire details of the flow pattern locally
such as film thickness and plug length and estimate the interfacial area (Ghaini et al 2010 Xu et al
2013)
One of the separations that can benefit from operation in small channels is the extraction of lanthanides
from acidic solutions Lanthanides with their strong photoluminescence and magnetic properties are
important to many industrial applications Europium and yttrium oxides can be used as fluorescing agents
for anodic rays in television and monitor screens (Lee and Yang 1995) Lanthanide oxides are used to
colour ceramics and glasses (Goonan 2011) Some compounds of lanthanides find applications as
catalysts for example oxides of thorium and cerium are used in the conversion of crude oil into common
consumer products (Lew 2010) Lanthanides have also been used to regulate nuclear reactors as control
rods because they absorb neutrons (Kučera et al 2007) and to make strong permanent magnets (Wang et
al 2011) Scarcity on natural resources means that the large quantities of lanthanides present in
electronic waste such as spent fluorescent lamps (Rabah 2008) computer monitor scraps (Resende and
Morais 2010) and colour TV tubes (De Morais 2000) need to be recycled In the field of spent nuclear
fuel reprocessing recovery of the trivalent actinides and lanthanides is a key step in high-level waste
management Since trivalent lanthanides cannot be extracted by TBP they are rejected to high-level
liquid waste in the PUREX process (Rout et al 2011a) They can however be extracted by the TRUEX
solvent which is a mixture of 02 M CMOP- 12 M TBP in n-dodecane (Horwitz et al 1982 Schulz and
Horwitz 1986)
3
Further intensification of the extraction process can be achieved by using room temperature ionic liquids
(RTILs or ILs) which have emerged as alternatives to organic solvents for catalytic reactions and
separations Ionic liquids are salts with very low vapour pressure that can dissolve a wide range of
organic and inorganic compounds It has been found that when ILs are used in extractions as diluents in
conjunction with appropriate extractants the partition coefficients for lanthanides are increased compared
to conventional solvents(Chun et al 2001 Okamura et al 2012 Rout et al 2012) The distribution ratio
of Eu(III) in CMPO-TBP[C4min][NTf2] can be 10 times larger than when n-dodecane (n-DD)is
used(Rout et al 2011a) Nakashima et al (2003)studied the extraction behaviour of trivalent lanthanides
in the presence of CMPOC4mimPF6 and found that use of ILs as the diluent of the extracting phase can
reduce extractant consumption compared to a conventional solvent (n-DD) However the industrial use
of ionic liquidsis still limited because of their high production costs This barrier can be overcome with
the use of the small scale separators which intensify mass transfer and can lead to the reduction of the
amount of solvent required
In this work the continuous extraction of Eu from nitric acid solutions is studied for the first time in
microchannels using an ionic liquid solution (02M CMPO-12M TBP[C4mim][NTf2]) as the extraction
phase In what follows the experimental set up and methodology are presented and the high speed
imaging and bright field Particle Image Velocimetry (PIV) techniques that are used to study the
hydrodynamic characteristics of the plug flow are discussed Results are then shown on europium
extraction efficiencies and mass transfer coefficients and are related to the geometric parameters of the
plug flow and the circulation patterns inside the plugs The mass transfer coefficients are also compared
against literature correlations and values from conventional large scale systems
2 Materials and experimental methodologies
In this study the continuous extraction of Eu(III) from nitric acid solutions to a
CMPOTBP[C4mim][NTf2] solution was carried out in 02 mm and 05 mm ID capillary channels The
ionic liquid [C4min][NTf2] with viscosity of 0052 Pa∙s and density of 1420 kg∙m-3 was obtained from
the QUILL Research Centre Queenrsquos University of Belfast The tri-n-butylphosphate (TBP) which acts
as a modifier to prevent the formation of lsquocrud-typersquo precipitate (Rout et al 2011b) was purchased from
Sigma-Aldrich CMPO was used as extractant and obtained from Carbosynth Limited For the
preparation of the ionic liquid phase certain amount of CMPO was added into TBP and the mixture was
mechanically shaken for 2 hours Then the mixture was introduced into the ionic liquid [C4min][NTf2]and
stirred The concentrations of CMPO and TBP in the ionic liquid were equal to 02M and 12 M
respectively Various standard nitric acid solutions were obtained from Sigma-Aldrich and used as
4
aqueous phase The ionic liquid was pre-equilibrated with the desired concentration of nitric acid solution
before extraction because both H+ and NO3-can dissolve in the IL phase The solubility of H+ and NO3-
into the ionic liquid follows a physical absorption than a chemical extraction mechanism(Billard et al
2011b) and neither TBP nor CMPO influence it The fluid properties of the ionic liquid (02M
CMPO-12M TBP[C4min][NTf2]) and aqueous solutions (1M nitric acid) are summarized in Table 1
(measured at UCL laboratory) Each measurement was repeated 3 times to ensure reproducibility The
liquid viscosity and density were measured with a digital DV-III Ultra Rheometer (Brookfield UK) and a
DMA 5000 density meter (Anton Paar UK) respectively The interfacial tension was measured using a
DSA 100 drop analyzer (Kruss GmbH Germany) The refractive index was measured with an Abbe 5
Refractometer (Bellingham and Stanley UK) The diffusion coefficient of Eu(III) in the aqueous and
ionic liquid phases was obtained from the literature(Matsumiya et al 2008 Rao et al 2009 Ribeiro et
al 2011 Sengupta et al 2012 Yang et al 2014)
21 Experimental apparatus
A sketch of the experimental set up is shown in Fig1 Two Kds Legato syringe pumps (KD Science Inc
USA) were used to feed the two liquid mixtures to a T-junction with an error of 1 The aqueous phase
was injected perpendicular to the channel axis and the ionic liquid phase was introduced at the axis of the
main channel A sketch of circular 02 mm ID microchip made of Quartz from top view is shown in Fig 2
The main channel length (CL) for the 05 mm ID capillary varied from 5 to 25 cm The different lengths
were used to vary the residence time in the extractor without changing the mixture velocity which can
affect the flow pattern Both phases were introduced at the same volumetric flow rate which varied from
Qaq=QIL=0653 to 21205 mlhr Plug flow formed in all cases studied with the aqueous solution forming
always the dispersed plugs and the ionic liquid the continuous phase At the channel exit a flow splitter
with a PTFE channel as the main branch and a stainless steel channel as the side branch was used to
separate the two phases continuously (for details see Scheiff et al (2011) Tsaoulidis et al (2013)) An
Asia FLLEX module (Syrris Ltd UK) was also used as a continuous phase separator operated by
adjusting the pressure differential across a hydrophobic PTFE membrane This separator could not be
used at high flow rates though because of high pressure drops The separated phases were analyzed for
Eu(III) concentration in a USB2000+ UV-Vis spectrometer (Ocean Optics UK) After each set of
experiments the microchannel was cleaned with dichloromethane to remove any residual ionic liquid
then with acetone to remove any dichloromethane left At last compressed air was injected to the channel
to ensure that all the chemicals have been cleaned All experiments were conducted under ambient
temperature (238-255degC)
5
High speed imaging was used to study the hydrodynamic characteristics of the two phase system (Fig 1)
A 60-Watt continuous arc lamp was used to volumetrically illuminate the microchannel from the back
and a diffuser plane was added between the backlight and the test section for uniform illumination To
minimize optical distortions an acrylic box filled with water was put around the channel Because of the
background illumination the interface appears as a shadow which is captured by a high speed camera
(Photron Fastcam-Ultima APX UK) with adjustable image recording frequency from 2000 to 8000Hz
depending on flowrates The camera was coupled with an air-immersion long working distance objective
lens with magnification M=3 to 10 depending on the channel dimension In addition a bright field
Particle Image Velocimetry technique was applied with the same optical set up to obtain the velocity
profiles within the aqueous plugs For the velocity measurements the aqueous phase was seeded with
3μm polystyrene particles and their shadow was recorded by the high speed camera (resolution
1024X1024 pix2) The Insight 4G (TSI instrument) software was used to pre-process and capture the
images while data analysis was carried out with an in-house MATLAB code A median filter was applied
to the images to eliminate any background noise The displacement of tracer particles between two
consecutive frames was calculated to obtain velocity vectors using a square domain discretization of 32 X
32 pixels with 50 overlap to satisfy the Nyquist sampling criterion(Dore et al 2012) with velocity
spatial resolution of 2672 μm times 2672 μm in the 05 mm channel The correlation peak position was
computed with Gaussian peak algorithm detection and the validation of the velocity vectors was based on
standard deviation and primary to secondary peak vectors Removed false vectors were replaced with the
median value of neighboring velocity vectors (Chinaud et al 2015)
22 Chemical mechanisms
The chemical structure of [C4min][NTf2] ionic liquid is shown in Fig3 The stoichiometry of
metal-solvate in the ionic liquid phase varies from 13 (Eu CMPO) at trace levels to 11 at higher Eu(III)
loadings It is determined by the slope analysis of logDEu against log[CMPO]org(Rout et al 2011b)
where species with overline exist in the ionic liquid phase only
Eu3+ + xCMPO + 3NO3minus harr Eu(NO3)3 ∙ (CMPO)x
(1)
However the equilibrium often involves ion exchange between the aqueous and the ionic liquid phases
Billard et al (2011a) found that the cation part of the ionic liquid C4mim+ was present into the aqueous
phase after extraction By dissolving C4mimCl into the aqueous phase it was shown that the presence of
C4mim+ reduced the extraction efficiency (Nakashima et al 2005) In some cases anion exchange was
also observed for example Tf2N- transferred to aqueous Htta solution when Eu(III) was extracted from
ionic liquid (Okamura et al 2012) However there is no clear evidence of anion exchange when ionic
liquid acts as diluent because Tf2N- is a weakly coordinating anion (Binnemans 2007) According to the
6
above the mechanism can be written as
Eu3+ + xCMPO + 3NO3minus + 3C4mim+ harr Eu(NO3)3 ∙ (CMPO)x
+ 3C4mim+ (2)
When ILs are used to recover Eu(III) in conjunction with neutral extractants the reaction takes place in
the ionic liquid phase and not in the aqueous phase as it happens with conventional solvents Very limited
research is available on the extraction kinetics of Eu(III) coupled with ionic liquid The separations of
certain rare earth metals are characterized by fast reaction but slow mass transfer using conventional
organic solutions (Sarkar et al 1980) When ionic liquids are used however this may not be the case
due to their unique ion exchange mechanisms Brigham (2013) investigated lanthanide extraction by
HDEHP in n-dodecane from DTPA and found that the reaction follows pseudo first- or second-order
kinetics The second order rate constant of Eu(III) extraction was about 104 M-1s-1 which falls into the
range of fast reactions (1 to 1010 M-1s-1(Caldin 2001)) Therefore the present extraction system was
treated as fast reaction although further research is still needed to accurately describe it
3 Results and Discussion
31 Specific interfacial area
The rate of mass transfer between two phases depends on the interfacial area available For the
calculation of the interfacial area in plug flow it is assumed that the dispersed plugs have a cylindrical
body and hemispherical caps at the front and back When a continuous film is a present at the channel
wall the interfacial area can be calculated as follows with an error of less than 10(Raimondi et al
2014)
120572119901 =4119882119901(119871119875minus119908119901)+120587119882119901
2
1198711198801198621198681198632 (3)
where Luc is the unit cell length (one slug and one plug) and Wp and Lp represent the plug width and
length respectively The plug geometric parameters for each set of flow rates were obtained by averaging
results from 30 plugs with deviations between 425-710for film thickness and 533-952 for plug
and unit cell length
The effect of mixture velocity on interfacial area can be seen in Fig4 for equal flow rates of the two
phases from Qaq=QIL=3534 to 2121 mlh The interfacial area was found to increase slightly with
increasing Umix As the mixture velocity increases the plug formation frequency increases while shorter
plugs form which results in larger interfacial area values However the capillary diameter has a more
profound effect the interfacial area in the large channel is almost 3 times smaller than in the small one
7
for the same mixture velocity It has been suggested that the organic film can be ignored during mass
transfer at low mixture velocities (Ghaini et al 2010) However when ionic liquid is the continuous
phase the film (δfilmR = 01585-03022 where δfilm and R are film thickness and channel radius
respectively) is thicker than with conventional organic solvents (δfilm R = 00928-01295) and may affect
mass transfer
32 Distribution coefficients for Eu(III) extraction
To characterize the mass transfer process a number of parameters will be used The Eu(III) distribution
coefficient DEu is defined as the ratio of concentration of europium in the ionic liquid phase to the
concentration in the aqueous phase
119863119864119906 =119862119886119902119894119899119894minus119862119886119902
119890
119862119886119902119890 (4)
The Eu(III) distribution coefficients for the aqueous-ionic liquid system were measured at different nitric
acid concentrations (001 01 05 10 and 20M) In the experiments equal volumes of nitric acid
solution containing europium nitrate and of ionic liquid solution (02M CMPO-12M TBP[C4min][NTf2])
were mechanically shaken for 3 hours The initial loading of Eu(III) in the aqueous phase was 20 30 and
50 mgmL respectively After equilibrium the Eu(III) concentration was measured in the aqueous phase
in a UV-Vis spectrometer Fig5 illustrates the Eu(III) distribution coefficient (DEu) as a function of initial
nitric acid concentration (Caqini) Each equilibrium experiment was repeated 5 times The relative
deviation was quite large for the low Eu(III) loading (20mgmL) ranging between 369 and 2876
but decreased to 255 - 1418 at 50 mgmL loading where the absorption signal in the UV-Vis is
stronger and more stable than at lower loadings The Eu(III) concentration in the ionic liquid phase was
also measured with UV-Vis The amount after extraction was between 8965 to 10154 of the initial
Eu(III) loading It would be difficult to have better agreement because the IL cations the NO3-or the
impurities in the imidazolium-based ionic liquids also have absorption characteristics in the UV range
that can mask the Eu(III) signal (Billard et al 2011a)
As can be seen from Fig5 the distribution coefficient reduces with increasing Eu(III) loading which
means that the Eu(III) in the aqueous phase is more difficult to be distributed into the ionic liquid phase
However 50 mgmL concentration was chosen for the microchannel extraction experiments because of
the low concentration measurement errors Furthermore the distribution coefficient has its highest value
at 10M nitric acid concentration for all initial Eu(III) loadings which is in agreement with the results by
Rout et al (2011b) The distribution coefficients obtained when ionic liquid is used are by a factor of 10
higher to those achieved with the conventional TUREX solvent (02M CMPO-12M TBPn-DD) (Rout et
8
al 2011a)
33 Mass transfer in continuous extraction
The performance of a mass transfer unit is characterized by the mass transfer coefficient (KLa) The
driving force for mass transfer will vary along the length of the microchannel and a log mean
concentration difference (LMCD) can be used defined as
∆119871119872119862119863=(119862119886119902119894119899119894
119890 minus 119862119886119902119894119899119894) minus (119862119886119902119891119894119899119890 minus 119862119886119902119891119894119899)
ln(119862119886119902119894119899119894119890 minus 119862119886119902119894119899)(119862119886119902119891119894119899
119890 minus 119862119886119902119891119894119899)(5)
The mean value of the mass transfer flux can be written as
119873 = 119870119871∆119871119872119862119863 (6)
The mean value of the mass transfer flux is also equal to
=119928119938119954(119914119938119954119943119946119951minus119914119938119954119946119951)
119933120630119953(7)
By combining Eqn (6) and Eqn (7) and integrating from the initial (119862119886119902119894119899119894) to the final concentration
(119862119886119902119891119894119899) for time between 0 and the residence time τ the overall mass transfer coefficient is found
119870119871120572 =1
(1+1
119863119864119906
119876119886119902
119876119900119903119892)120591
ln (119862119886119902119891119894119899minus119862119886119902
119890
119862119886119902119894119899minus119862119886119902119890 ) (8)
The extraction efficiency Eeff refers to the ratio of the amount of species transferred to the maximum
amount transferable
119864119890119891119891 =Amount transferred
Maximum amount transferable=
119862119886119902119894119899minus119862119886119902119891119894119899
119862119886119902119894119899minus119862119886119902119890 (9)
The efficiency is a good indicator of the mass transfer performance of the contactor at various contact
times (Bapat and Tavlarides 1985 Dehkordi 2001) The extraction efficiency depends not only on the
overall volumetric mass transfer coefficient (KLa ) but also on the residence time (τ)
The overall volumetric mass transfer coefficients of the Eu(III) extraction in the 05 mm ID microchannel
calculated from Eqn (8) are shown in Fig6a as a function of residence time To obtain different
residence times (τ) the channel length was varied from 5 cm 15 cm to 25 cm at the same volumetric
flow rates of the two liquids Qaq= QIL=3534 mlhr The volumetric mass transfer coefficient was found to
decrease non-linearly with increasing residence time On average the mass transfer coefficient of τ=10s
(CL=5 cm) was 15 times higher than that of τ=30 s (CL=15 cm) under all nitric acid solutions while the
change between τ=30 s and τ=50 s (CL=25 cm) was small This suggests that the mass transfer at the inlet
of the channel contributes significantly to the overall mass transfer in the separation unit The nitric acid
9
concentration affects the mass transfer coefficient in a similar way that it affects the distribution
coefficient (Fig 5) The highest mass transfer was found at 10M nitric acid concentration followed by
the 05 and 20 M concentrations The lowest KLa were found for 01M nitric acid concentration
The effect of residence time on extraction efficiency can be seen in Fig6b In all cases the extraction
efficiency increases with residence time In the shortest channel (CL=5 cm and τ=10 s) the extraction
efficiency is relatively low (4355) despite the high mass transfer coefficients The highest Eeff was
found at 1M nitric acid concentration and at the longest residence time where it reaches 7150 of the
equilibrium value
34 Effect of mixture velocity on Eu(III) microfluidic extraction
The effect of mixture velocity on overall volumetric mass transfer coefficient was investigated in the
05mm ID microchannel (CL=15 cm) at varying nitric acid concentrations for equal volumetric flow
rates of the two phases ranging from Qaq=QIL=3534 to 2121 mlhr As can be seen in Fig7 for 1M nitric
acid concentration the mass transfer coefficient increases with increasing mixture velocity which means
the extraction system is mass transfer dominated The increase in the mass transfer coefficient is partly
attributed to the small increase in interfacial area (see Fig4) This contribution however is small for
example the area increases by 464 when the mass transfer coefficient rises by 54 for change in
velocity from 05 to 3 cms Mixture velocity affects mass transfer in plug flow via two mechanisms(a)
convection due to internal circulation in the plugs and slugs (b) molecular diffusion due to concentration
gradients adjacent to the interface (Kashid et al 2007 Dessimoz et al 2008) The increase in mixture
velocity increases the intensity of internal circulation and enhances convective mass transfer (Tsaoulidis
and Angeli 2015) The circulation also helps interface renewal that increases the concentration gradients
and therefore mass transfer close to the interface The mass transfer performance however does not
depend only on mixture velocity and as can be seen at nitric acid concentration different from 1M the
effect of mixture velocity on the mass transfer coefficient is less significant The extraction of Eu(III) is a
physical process combined with chemical reaction and depends on both mass transfer and intrinsic
reaction kinetics (Xu et al 2013)
To evaluate the role of film thickness on mass transfer van Baten and Krishna (2004) proposed different
correlations for mass transfer from the plug caps and the film in the plug flow regime
119870119871119888119886119901 = 2radic2
120587radic
119863119880119875
119889119888 (10)
119870119871119891119894119897119898 = 2radic119863
120587119905119891119894119897119898
119897119899(1 ∆frasl )
(1minus∆) Folt 01 (short contact) (11)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
2
Assmann et al 2013 Xu et al 2013 Yang et al 2013)As extraction efficiencies depend on
concentration gradients interfacial area and residence times (Okubo et al 2008) the exact flow pattern
within the separation unit becomes important Plug (or segmented) flow in particular where one phase
forms dispersed plugs with diameter larger than the channel size separated by continuous phase slugs is a
preferred pattern because the circulation patterns forming in the two phases and the thin films separating
the plugs from the channel wall enhance mass transfer (Burns and Ramshaw 2001 Kashid et al 2005
Okubo et al 2008 Jovanović et al 2012) In addition the dispersed plug sizes are very regular and can
be controlled via the choice of the inlet geometry which further reduces non-uniformities common in
large scale extraction units such as mixers-settlers(Khakpay et al 2009) Knowledge of the interfacial
area is very important in the understanding and modelling of extraction operations Chemical reactions
eg alkaline hydrolysis of esters have been used to obtain global values of interfacial area in units such
as agitated contactors(Fernandes and Sharma 1967) packed columns(Puranik and Sharma 1970 Verma
and Sharma 1975)and two-impinging-stream reactors(Dehkordi 2002)In small channels where flow
patterns are well defined high speed imaging can be used to acquire details of the flow pattern locally
such as film thickness and plug length and estimate the interfacial area (Ghaini et al 2010 Xu et al
2013)
One of the separations that can benefit from operation in small channels is the extraction of lanthanides
from acidic solutions Lanthanides with their strong photoluminescence and magnetic properties are
important to many industrial applications Europium and yttrium oxides can be used as fluorescing agents
for anodic rays in television and monitor screens (Lee and Yang 1995) Lanthanide oxides are used to
colour ceramics and glasses (Goonan 2011) Some compounds of lanthanides find applications as
catalysts for example oxides of thorium and cerium are used in the conversion of crude oil into common
consumer products (Lew 2010) Lanthanides have also been used to regulate nuclear reactors as control
rods because they absorb neutrons (Kučera et al 2007) and to make strong permanent magnets (Wang et
al 2011) Scarcity on natural resources means that the large quantities of lanthanides present in
electronic waste such as spent fluorescent lamps (Rabah 2008) computer monitor scraps (Resende and
Morais 2010) and colour TV tubes (De Morais 2000) need to be recycled In the field of spent nuclear
fuel reprocessing recovery of the trivalent actinides and lanthanides is a key step in high-level waste
management Since trivalent lanthanides cannot be extracted by TBP they are rejected to high-level
liquid waste in the PUREX process (Rout et al 2011a) They can however be extracted by the TRUEX
solvent which is a mixture of 02 M CMOP- 12 M TBP in n-dodecane (Horwitz et al 1982 Schulz and
Horwitz 1986)
3
Further intensification of the extraction process can be achieved by using room temperature ionic liquids
(RTILs or ILs) which have emerged as alternatives to organic solvents for catalytic reactions and
separations Ionic liquids are salts with very low vapour pressure that can dissolve a wide range of
organic and inorganic compounds It has been found that when ILs are used in extractions as diluents in
conjunction with appropriate extractants the partition coefficients for lanthanides are increased compared
to conventional solvents(Chun et al 2001 Okamura et al 2012 Rout et al 2012) The distribution ratio
of Eu(III) in CMPO-TBP[C4min][NTf2] can be 10 times larger than when n-dodecane (n-DD)is
used(Rout et al 2011a) Nakashima et al (2003)studied the extraction behaviour of trivalent lanthanides
in the presence of CMPOC4mimPF6 and found that use of ILs as the diluent of the extracting phase can
reduce extractant consumption compared to a conventional solvent (n-DD) However the industrial use
of ionic liquidsis still limited because of their high production costs This barrier can be overcome with
the use of the small scale separators which intensify mass transfer and can lead to the reduction of the
amount of solvent required
In this work the continuous extraction of Eu from nitric acid solutions is studied for the first time in
microchannels using an ionic liquid solution (02M CMPO-12M TBP[C4mim][NTf2]) as the extraction
phase In what follows the experimental set up and methodology are presented and the high speed
imaging and bright field Particle Image Velocimetry (PIV) techniques that are used to study the
hydrodynamic characteristics of the plug flow are discussed Results are then shown on europium
extraction efficiencies and mass transfer coefficients and are related to the geometric parameters of the
plug flow and the circulation patterns inside the plugs The mass transfer coefficients are also compared
against literature correlations and values from conventional large scale systems
2 Materials and experimental methodologies
In this study the continuous extraction of Eu(III) from nitric acid solutions to a
CMPOTBP[C4mim][NTf2] solution was carried out in 02 mm and 05 mm ID capillary channels The
ionic liquid [C4min][NTf2] with viscosity of 0052 Pa∙s and density of 1420 kg∙m-3 was obtained from
the QUILL Research Centre Queenrsquos University of Belfast The tri-n-butylphosphate (TBP) which acts
as a modifier to prevent the formation of lsquocrud-typersquo precipitate (Rout et al 2011b) was purchased from
Sigma-Aldrich CMPO was used as extractant and obtained from Carbosynth Limited For the
preparation of the ionic liquid phase certain amount of CMPO was added into TBP and the mixture was
mechanically shaken for 2 hours Then the mixture was introduced into the ionic liquid [C4min][NTf2]and
stirred The concentrations of CMPO and TBP in the ionic liquid were equal to 02M and 12 M
respectively Various standard nitric acid solutions were obtained from Sigma-Aldrich and used as
4
aqueous phase The ionic liquid was pre-equilibrated with the desired concentration of nitric acid solution
before extraction because both H+ and NO3-can dissolve in the IL phase The solubility of H+ and NO3-
into the ionic liquid follows a physical absorption than a chemical extraction mechanism(Billard et al
2011b) and neither TBP nor CMPO influence it The fluid properties of the ionic liquid (02M
CMPO-12M TBP[C4min][NTf2]) and aqueous solutions (1M nitric acid) are summarized in Table 1
(measured at UCL laboratory) Each measurement was repeated 3 times to ensure reproducibility The
liquid viscosity and density were measured with a digital DV-III Ultra Rheometer (Brookfield UK) and a
DMA 5000 density meter (Anton Paar UK) respectively The interfacial tension was measured using a
DSA 100 drop analyzer (Kruss GmbH Germany) The refractive index was measured with an Abbe 5
Refractometer (Bellingham and Stanley UK) The diffusion coefficient of Eu(III) in the aqueous and
ionic liquid phases was obtained from the literature(Matsumiya et al 2008 Rao et al 2009 Ribeiro et
al 2011 Sengupta et al 2012 Yang et al 2014)
21 Experimental apparatus
A sketch of the experimental set up is shown in Fig1 Two Kds Legato syringe pumps (KD Science Inc
USA) were used to feed the two liquid mixtures to a T-junction with an error of 1 The aqueous phase
was injected perpendicular to the channel axis and the ionic liquid phase was introduced at the axis of the
main channel A sketch of circular 02 mm ID microchip made of Quartz from top view is shown in Fig 2
The main channel length (CL) for the 05 mm ID capillary varied from 5 to 25 cm The different lengths
were used to vary the residence time in the extractor without changing the mixture velocity which can
affect the flow pattern Both phases were introduced at the same volumetric flow rate which varied from
Qaq=QIL=0653 to 21205 mlhr Plug flow formed in all cases studied with the aqueous solution forming
always the dispersed plugs and the ionic liquid the continuous phase At the channel exit a flow splitter
with a PTFE channel as the main branch and a stainless steel channel as the side branch was used to
separate the two phases continuously (for details see Scheiff et al (2011) Tsaoulidis et al (2013)) An
Asia FLLEX module (Syrris Ltd UK) was also used as a continuous phase separator operated by
adjusting the pressure differential across a hydrophobic PTFE membrane This separator could not be
used at high flow rates though because of high pressure drops The separated phases were analyzed for
Eu(III) concentration in a USB2000+ UV-Vis spectrometer (Ocean Optics UK) After each set of
experiments the microchannel was cleaned with dichloromethane to remove any residual ionic liquid
then with acetone to remove any dichloromethane left At last compressed air was injected to the channel
to ensure that all the chemicals have been cleaned All experiments were conducted under ambient
temperature (238-255degC)
5
High speed imaging was used to study the hydrodynamic characteristics of the two phase system (Fig 1)
A 60-Watt continuous arc lamp was used to volumetrically illuminate the microchannel from the back
and a diffuser plane was added between the backlight and the test section for uniform illumination To
minimize optical distortions an acrylic box filled with water was put around the channel Because of the
background illumination the interface appears as a shadow which is captured by a high speed camera
(Photron Fastcam-Ultima APX UK) with adjustable image recording frequency from 2000 to 8000Hz
depending on flowrates The camera was coupled with an air-immersion long working distance objective
lens with magnification M=3 to 10 depending on the channel dimension In addition a bright field
Particle Image Velocimetry technique was applied with the same optical set up to obtain the velocity
profiles within the aqueous plugs For the velocity measurements the aqueous phase was seeded with
3μm polystyrene particles and their shadow was recorded by the high speed camera (resolution
1024X1024 pix2) The Insight 4G (TSI instrument) software was used to pre-process and capture the
images while data analysis was carried out with an in-house MATLAB code A median filter was applied
to the images to eliminate any background noise The displacement of tracer particles between two
consecutive frames was calculated to obtain velocity vectors using a square domain discretization of 32 X
32 pixels with 50 overlap to satisfy the Nyquist sampling criterion(Dore et al 2012) with velocity
spatial resolution of 2672 μm times 2672 μm in the 05 mm channel The correlation peak position was
computed with Gaussian peak algorithm detection and the validation of the velocity vectors was based on
standard deviation and primary to secondary peak vectors Removed false vectors were replaced with the
median value of neighboring velocity vectors (Chinaud et al 2015)
22 Chemical mechanisms
The chemical structure of [C4min][NTf2] ionic liquid is shown in Fig3 The stoichiometry of
metal-solvate in the ionic liquid phase varies from 13 (Eu CMPO) at trace levels to 11 at higher Eu(III)
loadings It is determined by the slope analysis of logDEu against log[CMPO]org(Rout et al 2011b)
where species with overline exist in the ionic liquid phase only
Eu3+ + xCMPO + 3NO3minus harr Eu(NO3)3 ∙ (CMPO)x
(1)
However the equilibrium often involves ion exchange between the aqueous and the ionic liquid phases
Billard et al (2011a) found that the cation part of the ionic liquid C4mim+ was present into the aqueous
phase after extraction By dissolving C4mimCl into the aqueous phase it was shown that the presence of
C4mim+ reduced the extraction efficiency (Nakashima et al 2005) In some cases anion exchange was
also observed for example Tf2N- transferred to aqueous Htta solution when Eu(III) was extracted from
ionic liquid (Okamura et al 2012) However there is no clear evidence of anion exchange when ionic
liquid acts as diluent because Tf2N- is a weakly coordinating anion (Binnemans 2007) According to the
6
above the mechanism can be written as
Eu3+ + xCMPO + 3NO3minus + 3C4mim+ harr Eu(NO3)3 ∙ (CMPO)x
+ 3C4mim+ (2)
When ILs are used to recover Eu(III) in conjunction with neutral extractants the reaction takes place in
the ionic liquid phase and not in the aqueous phase as it happens with conventional solvents Very limited
research is available on the extraction kinetics of Eu(III) coupled with ionic liquid The separations of
certain rare earth metals are characterized by fast reaction but slow mass transfer using conventional
organic solutions (Sarkar et al 1980) When ionic liquids are used however this may not be the case
due to their unique ion exchange mechanisms Brigham (2013) investigated lanthanide extraction by
HDEHP in n-dodecane from DTPA and found that the reaction follows pseudo first- or second-order
kinetics The second order rate constant of Eu(III) extraction was about 104 M-1s-1 which falls into the
range of fast reactions (1 to 1010 M-1s-1(Caldin 2001)) Therefore the present extraction system was
treated as fast reaction although further research is still needed to accurately describe it
3 Results and Discussion
31 Specific interfacial area
The rate of mass transfer between two phases depends on the interfacial area available For the
calculation of the interfacial area in plug flow it is assumed that the dispersed plugs have a cylindrical
body and hemispherical caps at the front and back When a continuous film is a present at the channel
wall the interfacial area can be calculated as follows with an error of less than 10(Raimondi et al
2014)
120572119901 =4119882119901(119871119875minus119908119901)+120587119882119901
2
1198711198801198621198681198632 (3)
where Luc is the unit cell length (one slug and one plug) and Wp and Lp represent the plug width and
length respectively The plug geometric parameters for each set of flow rates were obtained by averaging
results from 30 plugs with deviations between 425-710for film thickness and 533-952 for plug
and unit cell length
The effect of mixture velocity on interfacial area can be seen in Fig4 for equal flow rates of the two
phases from Qaq=QIL=3534 to 2121 mlh The interfacial area was found to increase slightly with
increasing Umix As the mixture velocity increases the plug formation frequency increases while shorter
plugs form which results in larger interfacial area values However the capillary diameter has a more
profound effect the interfacial area in the large channel is almost 3 times smaller than in the small one
7
for the same mixture velocity It has been suggested that the organic film can be ignored during mass
transfer at low mixture velocities (Ghaini et al 2010) However when ionic liquid is the continuous
phase the film (δfilmR = 01585-03022 where δfilm and R are film thickness and channel radius
respectively) is thicker than with conventional organic solvents (δfilm R = 00928-01295) and may affect
mass transfer
32 Distribution coefficients for Eu(III) extraction
To characterize the mass transfer process a number of parameters will be used The Eu(III) distribution
coefficient DEu is defined as the ratio of concentration of europium in the ionic liquid phase to the
concentration in the aqueous phase
119863119864119906 =119862119886119902119894119899119894minus119862119886119902
119890
119862119886119902119890 (4)
The Eu(III) distribution coefficients for the aqueous-ionic liquid system were measured at different nitric
acid concentrations (001 01 05 10 and 20M) In the experiments equal volumes of nitric acid
solution containing europium nitrate and of ionic liquid solution (02M CMPO-12M TBP[C4min][NTf2])
were mechanically shaken for 3 hours The initial loading of Eu(III) in the aqueous phase was 20 30 and
50 mgmL respectively After equilibrium the Eu(III) concentration was measured in the aqueous phase
in a UV-Vis spectrometer Fig5 illustrates the Eu(III) distribution coefficient (DEu) as a function of initial
nitric acid concentration (Caqini) Each equilibrium experiment was repeated 5 times The relative
deviation was quite large for the low Eu(III) loading (20mgmL) ranging between 369 and 2876
but decreased to 255 - 1418 at 50 mgmL loading where the absorption signal in the UV-Vis is
stronger and more stable than at lower loadings The Eu(III) concentration in the ionic liquid phase was
also measured with UV-Vis The amount after extraction was between 8965 to 10154 of the initial
Eu(III) loading It would be difficult to have better agreement because the IL cations the NO3-or the
impurities in the imidazolium-based ionic liquids also have absorption characteristics in the UV range
that can mask the Eu(III) signal (Billard et al 2011a)
As can be seen from Fig5 the distribution coefficient reduces with increasing Eu(III) loading which
means that the Eu(III) in the aqueous phase is more difficult to be distributed into the ionic liquid phase
However 50 mgmL concentration was chosen for the microchannel extraction experiments because of
the low concentration measurement errors Furthermore the distribution coefficient has its highest value
at 10M nitric acid concentration for all initial Eu(III) loadings which is in agreement with the results by
Rout et al (2011b) The distribution coefficients obtained when ionic liquid is used are by a factor of 10
higher to those achieved with the conventional TUREX solvent (02M CMPO-12M TBPn-DD) (Rout et
8
al 2011a)
33 Mass transfer in continuous extraction
The performance of a mass transfer unit is characterized by the mass transfer coefficient (KLa) The
driving force for mass transfer will vary along the length of the microchannel and a log mean
concentration difference (LMCD) can be used defined as
∆119871119872119862119863=(119862119886119902119894119899119894
119890 minus 119862119886119902119894119899119894) minus (119862119886119902119891119894119899119890 minus 119862119886119902119891119894119899)
ln(119862119886119902119894119899119894119890 minus 119862119886119902119894119899)(119862119886119902119891119894119899
119890 minus 119862119886119902119891119894119899)(5)
The mean value of the mass transfer flux can be written as
119873 = 119870119871∆119871119872119862119863 (6)
The mean value of the mass transfer flux is also equal to
=119928119938119954(119914119938119954119943119946119951minus119914119938119954119946119951)
119933120630119953(7)
By combining Eqn (6) and Eqn (7) and integrating from the initial (119862119886119902119894119899119894) to the final concentration
(119862119886119902119891119894119899) for time between 0 and the residence time τ the overall mass transfer coefficient is found
119870119871120572 =1
(1+1
119863119864119906
119876119886119902
119876119900119903119892)120591
ln (119862119886119902119891119894119899minus119862119886119902
119890
119862119886119902119894119899minus119862119886119902119890 ) (8)
The extraction efficiency Eeff refers to the ratio of the amount of species transferred to the maximum
amount transferable
119864119890119891119891 =Amount transferred
Maximum amount transferable=
119862119886119902119894119899minus119862119886119902119891119894119899
119862119886119902119894119899minus119862119886119902119890 (9)
The efficiency is a good indicator of the mass transfer performance of the contactor at various contact
times (Bapat and Tavlarides 1985 Dehkordi 2001) The extraction efficiency depends not only on the
overall volumetric mass transfer coefficient (KLa ) but also on the residence time (τ)
The overall volumetric mass transfer coefficients of the Eu(III) extraction in the 05 mm ID microchannel
calculated from Eqn (8) are shown in Fig6a as a function of residence time To obtain different
residence times (τ) the channel length was varied from 5 cm 15 cm to 25 cm at the same volumetric
flow rates of the two liquids Qaq= QIL=3534 mlhr The volumetric mass transfer coefficient was found to
decrease non-linearly with increasing residence time On average the mass transfer coefficient of τ=10s
(CL=5 cm) was 15 times higher than that of τ=30 s (CL=15 cm) under all nitric acid solutions while the
change between τ=30 s and τ=50 s (CL=25 cm) was small This suggests that the mass transfer at the inlet
of the channel contributes significantly to the overall mass transfer in the separation unit The nitric acid
9
concentration affects the mass transfer coefficient in a similar way that it affects the distribution
coefficient (Fig 5) The highest mass transfer was found at 10M nitric acid concentration followed by
the 05 and 20 M concentrations The lowest KLa were found for 01M nitric acid concentration
The effect of residence time on extraction efficiency can be seen in Fig6b In all cases the extraction
efficiency increases with residence time In the shortest channel (CL=5 cm and τ=10 s) the extraction
efficiency is relatively low (4355) despite the high mass transfer coefficients The highest Eeff was
found at 1M nitric acid concentration and at the longest residence time where it reaches 7150 of the
equilibrium value
34 Effect of mixture velocity on Eu(III) microfluidic extraction
The effect of mixture velocity on overall volumetric mass transfer coefficient was investigated in the
05mm ID microchannel (CL=15 cm) at varying nitric acid concentrations for equal volumetric flow
rates of the two phases ranging from Qaq=QIL=3534 to 2121 mlhr As can be seen in Fig7 for 1M nitric
acid concentration the mass transfer coefficient increases with increasing mixture velocity which means
the extraction system is mass transfer dominated The increase in the mass transfer coefficient is partly
attributed to the small increase in interfacial area (see Fig4) This contribution however is small for
example the area increases by 464 when the mass transfer coefficient rises by 54 for change in
velocity from 05 to 3 cms Mixture velocity affects mass transfer in plug flow via two mechanisms(a)
convection due to internal circulation in the plugs and slugs (b) molecular diffusion due to concentration
gradients adjacent to the interface (Kashid et al 2007 Dessimoz et al 2008) The increase in mixture
velocity increases the intensity of internal circulation and enhances convective mass transfer (Tsaoulidis
and Angeli 2015) The circulation also helps interface renewal that increases the concentration gradients
and therefore mass transfer close to the interface The mass transfer performance however does not
depend only on mixture velocity and as can be seen at nitric acid concentration different from 1M the
effect of mixture velocity on the mass transfer coefficient is less significant The extraction of Eu(III) is a
physical process combined with chemical reaction and depends on both mass transfer and intrinsic
reaction kinetics (Xu et al 2013)
To evaluate the role of film thickness on mass transfer van Baten and Krishna (2004) proposed different
correlations for mass transfer from the plug caps and the film in the plug flow regime
119870119871119888119886119901 = 2radic2
120587radic
119863119880119875
119889119888 (10)
119870119871119891119894119897119898 = 2radic119863
120587119905119891119894119897119898
119897119899(1 ∆frasl )
(1minus∆) Folt 01 (short contact) (11)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
3
Further intensification of the extraction process can be achieved by using room temperature ionic liquids
(RTILs or ILs) which have emerged as alternatives to organic solvents for catalytic reactions and
separations Ionic liquids are salts with very low vapour pressure that can dissolve a wide range of
organic and inorganic compounds It has been found that when ILs are used in extractions as diluents in
conjunction with appropriate extractants the partition coefficients for lanthanides are increased compared
to conventional solvents(Chun et al 2001 Okamura et al 2012 Rout et al 2012) The distribution ratio
of Eu(III) in CMPO-TBP[C4min][NTf2] can be 10 times larger than when n-dodecane (n-DD)is
used(Rout et al 2011a) Nakashima et al (2003)studied the extraction behaviour of trivalent lanthanides
in the presence of CMPOC4mimPF6 and found that use of ILs as the diluent of the extracting phase can
reduce extractant consumption compared to a conventional solvent (n-DD) However the industrial use
of ionic liquidsis still limited because of their high production costs This barrier can be overcome with
the use of the small scale separators which intensify mass transfer and can lead to the reduction of the
amount of solvent required
In this work the continuous extraction of Eu from nitric acid solutions is studied for the first time in
microchannels using an ionic liquid solution (02M CMPO-12M TBP[C4mim][NTf2]) as the extraction
phase In what follows the experimental set up and methodology are presented and the high speed
imaging and bright field Particle Image Velocimetry (PIV) techniques that are used to study the
hydrodynamic characteristics of the plug flow are discussed Results are then shown on europium
extraction efficiencies and mass transfer coefficients and are related to the geometric parameters of the
plug flow and the circulation patterns inside the plugs The mass transfer coefficients are also compared
against literature correlations and values from conventional large scale systems
2 Materials and experimental methodologies
In this study the continuous extraction of Eu(III) from nitric acid solutions to a
CMPOTBP[C4mim][NTf2] solution was carried out in 02 mm and 05 mm ID capillary channels The
ionic liquid [C4min][NTf2] with viscosity of 0052 Pa∙s and density of 1420 kg∙m-3 was obtained from
the QUILL Research Centre Queenrsquos University of Belfast The tri-n-butylphosphate (TBP) which acts
as a modifier to prevent the formation of lsquocrud-typersquo precipitate (Rout et al 2011b) was purchased from
Sigma-Aldrich CMPO was used as extractant and obtained from Carbosynth Limited For the
preparation of the ionic liquid phase certain amount of CMPO was added into TBP and the mixture was
mechanically shaken for 2 hours Then the mixture was introduced into the ionic liquid [C4min][NTf2]and
stirred The concentrations of CMPO and TBP in the ionic liquid were equal to 02M and 12 M
respectively Various standard nitric acid solutions were obtained from Sigma-Aldrich and used as
4
aqueous phase The ionic liquid was pre-equilibrated with the desired concentration of nitric acid solution
before extraction because both H+ and NO3-can dissolve in the IL phase The solubility of H+ and NO3-
into the ionic liquid follows a physical absorption than a chemical extraction mechanism(Billard et al
2011b) and neither TBP nor CMPO influence it The fluid properties of the ionic liquid (02M
CMPO-12M TBP[C4min][NTf2]) and aqueous solutions (1M nitric acid) are summarized in Table 1
(measured at UCL laboratory) Each measurement was repeated 3 times to ensure reproducibility The
liquid viscosity and density were measured with a digital DV-III Ultra Rheometer (Brookfield UK) and a
DMA 5000 density meter (Anton Paar UK) respectively The interfacial tension was measured using a
DSA 100 drop analyzer (Kruss GmbH Germany) The refractive index was measured with an Abbe 5
Refractometer (Bellingham and Stanley UK) The diffusion coefficient of Eu(III) in the aqueous and
ionic liquid phases was obtained from the literature(Matsumiya et al 2008 Rao et al 2009 Ribeiro et
al 2011 Sengupta et al 2012 Yang et al 2014)
21 Experimental apparatus
A sketch of the experimental set up is shown in Fig1 Two Kds Legato syringe pumps (KD Science Inc
USA) were used to feed the two liquid mixtures to a T-junction with an error of 1 The aqueous phase
was injected perpendicular to the channel axis and the ionic liquid phase was introduced at the axis of the
main channel A sketch of circular 02 mm ID microchip made of Quartz from top view is shown in Fig 2
The main channel length (CL) for the 05 mm ID capillary varied from 5 to 25 cm The different lengths
were used to vary the residence time in the extractor without changing the mixture velocity which can
affect the flow pattern Both phases were introduced at the same volumetric flow rate which varied from
Qaq=QIL=0653 to 21205 mlhr Plug flow formed in all cases studied with the aqueous solution forming
always the dispersed plugs and the ionic liquid the continuous phase At the channel exit a flow splitter
with a PTFE channel as the main branch and a stainless steel channel as the side branch was used to
separate the two phases continuously (for details see Scheiff et al (2011) Tsaoulidis et al (2013)) An
Asia FLLEX module (Syrris Ltd UK) was also used as a continuous phase separator operated by
adjusting the pressure differential across a hydrophobic PTFE membrane This separator could not be
used at high flow rates though because of high pressure drops The separated phases were analyzed for
Eu(III) concentration in a USB2000+ UV-Vis spectrometer (Ocean Optics UK) After each set of
experiments the microchannel was cleaned with dichloromethane to remove any residual ionic liquid
then with acetone to remove any dichloromethane left At last compressed air was injected to the channel
to ensure that all the chemicals have been cleaned All experiments were conducted under ambient
temperature (238-255degC)
5
High speed imaging was used to study the hydrodynamic characteristics of the two phase system (Fig 1)
A 60-Watt continuous arc lamp was used to volumetrically illuminate the microchannel from the back
and a diffuser plane was added between the backlight and the test section for uniform illumination To
minimize optical distortions an acrylic box filled with water was put around the channel Because of the
background illumination the interface appears as a shadow which is captured by a high speed camera
(Photron Fastcam-Ultima APX UK) with adjustable image recording frequency from 2000 to 8000Hz
depending on flowrates The camera was coupled with an air-immersion long working distance objective
lens with magnification M=3 to 10 depending on the channel dimension In addition a bright field
Particle Image Velocimetry technique was applied with the same optical set up to obtain the velocity
profiles within the aqueous plugs For the velocity measurements the aqueous phase was seeded with
3μm polystyrene particles and their shadow was recorded by the high speed camera (resolution
1024X1024 pix2) The Insight 4G (TSI instrument) software was used to pre-process and capture the
images while data analysis was carried out with an in-house MATLAB code A median filter was applied
to the images to eliminate any background noise The displacement of tracer particles between two
consecutive frames was calculated to obtain velocity vectors using a square domain discretization of 32 X
32 pixels with 50 overlap to satisfy the Nyquist sampling criterion(Dore et al 2012) with velocity
spatial resolution of 2672 μm times 2672 μm in the 05 mm channel The correlation peak position was
computed with Gaussian peak algorithm detection and the validation of the velocity vectors was based on
standard deviation and primary to secondary peak vectors Removed false vectors were replaced with the
median value of neighboring velocity vectors (Chinaud et al 2015)
22 Chemical mechanisms
The chemical structure of [C4min][NTf2] ionic liquid is shown in Fig3 The stoichiometry of
metal-solvate in the ionic liquid phase varies from 13 (Eu CMPO) at trace levels to 11 at higher Eu(III)
loadings It is determined by the slope analysis of logDEu against log[CMPO]org(Rout et al 2011b)
where species with overline exist in the ionic liquid phase only
Eu3+ + xCMPO + 3NO3minus harr Eu(NO3)3 ∙ (CMPO)x
(1)
However the equilibrium often involves ion exchange between the aqueous and the ionic liquid phases
Billard et al (2011a) found that the cation part of the ionic liquid C4mim+ was present into the aqueous
phase after extraction By dissolving C4mimCl into the aqueous phase it was shown that the presence of
C4mim+ reduced the extraction efficiency (Nakashima et al 2005) In some cases anion exchange was
also observed for example Tf2N- transferred to aqueous Htta solution when Eu(III) was extracted from
ionic liquid (Okamura et al 2012) However there is no clear evidence of anion exchange when ionic
liquid acts as diluent because Tf2N- is a weakly coordinating anion (Binnemans 2007) According to the
6
above the mechanism can be written as
Eu3+ + xCMPO + 3NO3minus + 3C4mim+ harr Eu(NO3)3 ∙ (CMPO)x
+ 3C4mim+ (2)
When ILs are used to recover Eu(III) in conjunction with neutral extractants the reaction takes place in
the ionic liquid phase and not in the aqueous phase as it happens with conventional solvents Very limited
research is available on the extraction kinetics of Eu(III) coupled with ionic liquid The separations of
certain rare earth metals are characterized by fast reaction but slow mass transfer using conventional
organic solutions (Sarkar et al 1980) When ionic liquids are used however this may not be the case
due to their unique ion exchange mechanisms Brigham (2013) investigated lanthanide extraction by
HDEHP in n-dodecane from DTPA and found that the reaction follows pseudo first- or second-order
kinetics The second order rate constant of Eu(III) extraction was about 104 M-1s-1 which falls into the
range of fast reactions (1 to 1010 M-1s-1(Caldin 2001)) Therefore the present extraction system was
treated as fast reaction although further research is still needed to accurately describe it
3 Results and Discussion
31 Specific interfacial area
The rate of mass transfer between two phases depends on the interfacial area available For the
calculation of the interfacial area in plug flow it is assumed that the dispersed plugs have a cylindrical
body and hemispherical caps at the front and back When a continuous film is a present at the channel
wall the interfacial area can be calculated as follows with an error of less than 10(Raimondi et al
2014)
120572119901 =4119882119901(119871119875minus119908119901)+120587119882119901
2
1198711198801198621198681198632 (3)
where Luc is the unit cell length (one slug and one plug) and Wp and Lp represent the plug width and
length respectively The plug geometric parameters for each set of flow rates were obtained by averaging
results from 30 plugs with deviations between 425-710for film thickness and 533-952 for plug
and unit cell length
The effect of mixture velocity on interfacial area can be seen in Fig4 for equal flow rates of the two
phases from Qaq=QIL=3534 to 2121 mlh The interfacial area was found to increase slightly with
increasing Umix As the mixture velocity increases the plug formation frequency increases while shorter
plugs form which results in larger interfacial area values However the capillary diameter has a more
profound effect the interfacial area in the large channel is almost 3 times smaller than in the small one
7
for the same mixture velocity It has been suggested that the organic film can be ignored during mass
transfer at low mixture velocities (Ghaini et al 2010) However when ionic liquid is the continuous
phase the film (δfilmR = 01585-03022 where δfilm and R are film thickness and channel radius
respectively) is thicker than with conventional organic solvents (δfilm R = 00928-01295) and may affect
mass transfer
32 Distribution coefficients for Eu(III) extraction
To characterize the mass transfer process a number of parameters will be used The Eu(III) distribution
coefficient DEu is defined as the ratio of concentration of europium in the ionic liquid phase to the
concentration in the aqueous phase
119863119864119906 =119862119886119902119894119899119894minus119862119886119902
119890
119862119886119902119890 (4)
The Eu(III) distribution coefficients for the aqueous-ionic liquid system were measured at different nitric
acid concentrations (001 01 05 10 and 20M) In the experiments equal volumes of nitric acid
solution containing europium nitrate and of ionic liquid solution (02M CMPO-12M TBP[C4min][NTf2])
were mechanically shaken for 3 hours The initial loading of Eu(III) in the aqueous phase was 20 30 and
50 mgmL respectively After equilibrium the Eu(III) concentration was measured in the aqueous phase
in a UV-Vis spectrometer Fig5 illustrates the Eu(III) distribution coefficient (DEu) as a function of initial
nitric acid concentration (Caqini) Each equilibrium experiment was repeated 5 times The relative
deviation was quite large for the low Eu(III) loading (20mgmL) ranging between 369 and 2876
but decreased to 255 - 1418 at 50 mgmL loading where the absorption signal in the UV-Vis is
stronger and more stable than at lower loadings The Eu(III) concentration in the ionic liquid phase was
also measured with UV-Vis The amount after extraction was between 8965 to 10154 of the initial
Eu(III) loading It would be difficult to have better agreement because the IL cations the NO3-or the
impurities in the imidazolium-based ionic liquids also have absorption characteristics in the UV range
that can mask the Eu(III) signal (Billard et al 2011a)
As can be seen from Fig5 the distribution coefficient reduces with increasing Eu(III) loading which
means that the Eu(III) in the aqueous phase is more difficult to be distributed into the ionic liquid phase
However 50 mgmL concentration was chosen for the microchannel extraction experiments because of
the low concentration measurement errors Furthermore the distribution coefficient has its highest value
at 10M nitric acid concentration for all initial Eu(III) loadings which is in agreement with the results by
Rout et al (2011b) The distribution coefficients obtained when ionic liquid is used are by a factor of 10
higher to those achieved with the conventional TUREX solvent (02M CMPO-12M TBPn-DD) (Rout et
8
al 2011a)
33 Mass transfer in continuous extraction
The performance of a mass transfer unit is characterized by the mass transfer coefficient (KLa) The
driving force for mass transfer will vary along the length of the microchannel and a log mean
concentration difference (LMCD) can be used defined as
∆119871119872119862119863=(119862119886119902119894119899119894
119890 minus 119862119886119902119894119899119894) minus (119862119886119902119891119894119899119890 minus 119862119886119902119891119894119899)
ln(119862119886119902119894119899119894119890 minus 119862119886119902119894119899)(119862119886119902119891119894119899
119890 minus 119862119886119902119891119894119899)(5)
The mean value of the mass transfer flux can be written as
119873 = 119870119871∆119871119872119862119863 (6)
The mean value of the mass transfer flux is also equal to
=119928119938119954(119914119938119954119943119946119951minus119914119938119954119946119951)
119933120630119953(7)
By combining Eqn (6) and Eqn (7) and integrating from the initial (119862119886119902119894119899119894) to the final concentration
(119862119886119902119891119894119899) for time between 0 and the residence time τ the overall mass transfer coefficient is found
119870119871120572 =1
(1+1
119863119864119906
119876119886119902
119876119900119903119892)120591
ln (119862119886119902119891119894119899minus119862119886119902
119890
119862119886119902119894119899minus119862119886119902119890 ) (8)
The extraction efficiency Eeff refers to the ratio of the amount of species transferred to the maximum
amount transferable
119864119890119891119891 =Amount transferred
Maximum amount transferable=
119862119886119902119894119899minus119862119886119902119891119894119899
119862119886119902119894119899minus119862119886119902119890 (9)
The efficiency is a good indicator of the mass transfer performance of the contactor at various contact
times (Bapat and Tavlarides 1985 Dehkordi 2001) The extraction efficiency depends not only on the
overall volumetric mass transfer coefficient (KLa ) but also on the residence time (τ)
The overall volumetric mass transfer coefficients of the Eu(III) extraction in the 05 mm ID microchannel
calculated from Eqn (8) are shown in Fig6a as a function of residence time To obtain different
residence times (τ) the channel length was varied from 5 cm 15 cm to 25 cm at the same volumetric
flow rates of the two liquids Qaq= QIL=3534 mlhr The volumetric mass transfer coefficient was found to
decrease non-linearly with increasing residence time On average the mass transfer coefficient of τ=10s
(CL=5 cm) was 15 times higher than that of τ=30 s (CL=15 cm) under all nitric acid solutions while the
change between τ=30 s and τ=50 s (CL=25 cm) was small This suggests that the mass transfer at the inlet
of the channel contributes significantly to the overall mass transfer in the separation unit The nitric acid
9
concentration affects the mass transfer coefficient in a similar way that it affects the distribution
coefficient (Fig 5) The highest mass transfer was found at 10M nitric acid concentration followed by
the 05 and 20 M concentrations The lowest KLa were found for 01M nitric acid concentration
The effect of residence time on extraction efficiency can be seen in Fig6b In all cases the extraction
efficiency increases with residence time In the shortest channel (CL=5 cm and τ=10 s) the extraction
efficiency is relatively low (4355) despite the high mass transfer coefficients The highest Eeff was
found at 1M nitric acid concentration and at the longest residence time where it reaches 7150 of the
equilibrium value
34 Effect of mixture velocity on Eu(III) microfluidic extraction
The effect of mixture velocity on overall volumetric mass transfer coefficient was investigated in the
05mm ID microchannel (CL=15 cm) at varying nitric acid concentrations for equal volumetric flow
rates of the two phases ranging from Qaq=QIL=3534 to 2121 mlhr As can be seen in Fig7 for 1M nitric
acid concentration the mass transfer coefficient increases with increasing mixture velocity which means
the extraction system is mass transfer dominated The increase in the mass transfer coefficient is partly
attributed to the small increase in interfacial area (see Fig4) This contribution however is small for
example the area increases by 464 when the mass transfer coefficient rises by 54 for change in
velocity from 05 to 3 cms Mixture velocity affects mass transfer in plug flow via two mechanisms(a)
convection due to internal circulation in the plugs and slugs (b) molecular diffusion due to concentration
gradients adjacent to the interface (Kashid et al 2007 Dessimoz et al 2008) The increase in mixture
velocity increases the intensity of internal circulation and enhances convective mass transfer (Tsaoulidis
and Angeli 2015) The circulation also helps interface renewal that increases the concentration gradients
and therefore mass transfer close to the interface The mass transfer performance however does not
depend only on mixture velocity and as can be seen at nitric acid concentration different from 1M the
effect of mixture velocity on the mass transfer coefficient is less significant The extraction of Eu(III) is a
physical process combined with chemical reaction and depends on both mass transfer and intrinsic
reaction kinetics (Xu et al 2013)
To evaluate the role of film thickness on mass transfer van Baten and Krishna (2004) proposed different
correlations for mass transfer from the plug caps and the film in the plug flow regime
119870119871119888119886119901 = 2radic2
120587radic
119863119880119875
119889119888 (10)
119870119871119891119894119897119898 = 2radic119863
120587119905119891119894119897119898
119897119899(1 ∆frasl )
(1minus∆) Folt 01 (short contact) (11)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
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Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
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Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
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Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
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tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
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Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
4
aqueous phase The ionic liquid was pre-equilibrated with the desired concentration of nitric acid solution
before extraction because both H+ and NO3-can dissolve in the IL phase The solubility of H+ and NO3-
into the ionic liquid follows a physical absorption than a chemical extraction mechanism(Billard et al
2011b) and neither TBP nor CMPO influence it The fluid properties of the ionic liquid (02M
CMPO-12M TBP[C4min][NTf2]) and aqueous solutions (1M nitric acid) are summarized in Table 1
(measured at UCL laboratory) Each measurement was repeated 3 times to ensure reproducibility The
liquid viscosity and density were measured with a digital DV-III Ultra Rheometer (Brookfield UK) and a
DMA 5000 density meter (Anton Paar UK) respectively The interfacial tension was measured using a
DSA 100 drop analyzer (Kruss GmbH Germany) The refractive index was measured with an Abbe 5
Refractometer (Bellingham and Stanley UK) The diffusion coefficient of Eu(III) in the aqueous and
ionic liquid phases was obtained from the literature(Matsumiya et al 2008 Rao et al 2009 Ribeiro et
al 2011 Sengupta et al 2012 Yang et al 2014)
21 Experimental apparatus
A sketch of the experimental set up is shown in Fig1 Two Kds Legato syringe pumps (KD Science Inc
USA) were used to feed the two liquid mixtures to a T-junction with an error of 1 The aqueous phase
was injected perpendicular to the channel axis and the ionic liquid phase was introduced at the axis of the
main channel A sketch of circular 02 mm ID microchip made of Quartz from top view is shown in Fig 2
The main channel length (CL) for the 05 mm ID capillary varied from 5 to 25 cm The different lengths
were used to vary the residence time in the extractor without changing the mixture velocity which can
affect the flow pattern Both phases were introduced at the same volumetric flow rate which varied from
Qaq=QIL=0653 to 21205 mlhr Plug flow formed in all cases studied with the aqueous solution forming
always the dispersed plugs and the ionic liquid the continuous phase At the channel exit a flow splitter
with a PTFE channel as the main branch and a stainless steel channel as the side branch was used to
separate the two phases continuously (for details see Scheiff et al (2011) Tsaoulidis et al (2013)) An
Asia FLLEX module (Syrris Ltd UK) was also used as a continuous phase separator operated by
adjusting the pressure differential across a hydrophobic PTFE membrane This separator could not be
used at high flow rates though because of high pressure drops The separated phases were analyzed for
Eu(III) concentration in a USB2000+ UV-Vis spectrometer (Ocean Optics UK) After each set of
experiments the microchannel was cleaned with dichloromethane to remove any residual ionic liquid
then with acetone to remove any dichloromethane left At last compressed air was injected to the channel
to ensure that all the chemicals have been cleaned All experiments were conducted under ambient
temperature (238-255degC)
5
High speed imaging was used to study the hydrodynamic characteristics of the two phase system (Fig 1)
A 60-Watt continuous arc lamp was used to volumetrically illuminate the microchannel from the back
and a diffuser plane was added between the backlight and the test section for uniform illumination To
minimize optical distortions an acrylic box filled with water was put around the channel Because of the
background illumination the interface appears as a shadow which is captured by a high speed camera
(Photron Fastcam-Ultima APX UK) with adjustable image recording frequency from 2000 to 8000Hz
depending on flowrates The camera was coupled with an air-immersion long working distance objective
lens with magnification M=3 to 10 depending on the channel dimension In addition a bright field
Particle Image Velocimetry technique was applied with the same optical set up to obtain the velocity
profiles within the aqueous plugs For the velocity measurements the aqueous phase was seeded with
3μm polystyrene particles and their shadow was recorded by the high speed camera (resolution
1024X1024 pix2) The Insight 4G (TSI instrument) software was used to pre-process and capture the
images while data analysis was carried out with an in-house MATLAB code A median filter was applied
to the images to eliminate any background noise The displacement of tracer particles between two
consecutive frames was calculated to obtain velocity vectors using a square domain discretization of 32 X
32 pixels with 50 overlap to satisfy the Nyquist sampling criterion(Dore et al 2012) with velocity
spatial resolution of 2672 μm times 2672 μm in the 05 mm channel The correlation peak position was
computed with Gaussian peak algorithm detection and the validation of the velocity vectors was based on
standard deviation and primary to secondary peak vectors Removed false vectors were replaced with the
median value of neighboring velocity vectors (Chinaud et al 2015)
22 Chemical mechanisms
The chemical structure of [C4min][NTf2] ionic liquid is shown in Fig3 The stoichiometry of
metal-solvate in the ionic liquid phase varies from 13 (Eu CMPO) at trace levels to 11 at higher Eu(III)
loadings It is determined by the slope analysis of logDEu against log[CMPO]org(Rout et al 2011b)
where species with overline exist in the ionic liquid phase only
Eu3+ + xCMPO + 3NO3minus harr Eu(NO3)3 ∙ (CMPO)x
(1)
However the equilibrium often involves ion exchange between the aqueous and the ionic liquid phases
Billard et al (2011a) found that the cation part of the ionic liquid C4mim+ was present into the aqueous
phase after extraction By dissolving C4mimCl into the aqueous phase it was shown that the presence of
C4mim+ reduced the extraction efficiency (Nakashima et al 2005) In some cases anion exchange was
also observed for example Tf2N- transferred to aqueous Htta solution when Eu(III) was extracted from
ionic liquid (Okamura et al 2012) However there is no clear evidence of anion exchange when ionic
liquid acts as diluent because Tf2N- is a weakly coordinating anion (Binnemans 2007) According to the
6
above the mechanism can be written as
Eu3+ + xCMPO + 3NO3minus + 3C4mim+ harr Eu(NO3)3 ∙ (CMPO)x
+ 3C4mim+ (2)
When ILs are used to recover Eu(III) in conjunction with neutral extractants the reaction takes place in
the ionic liquid phase and not in the aqueous phase as it happens with conventional solvents Very limited
research is available on the extraction kinetics of Eu(III) coupled with ionic liquid The separations of
certain rare earth metals are characterized by fast reaction but slow mass transfer using conventional
organic solutions (Sarkar et al 1980) When ionic liquids are used however this may not be the case
due to their unique ion exchange mechanisms Brigham (2013) investigated lanthanide extraction by
HDEHP in n-dodecane from DTPA and found that the reaction follows pseudo first- or second-order
kinetics The second order rate constant of Eu(III) extraction was about 104 M-1s-1 which falls into the
range of fast reactions (1 to 1010 M-1s-1(Caldin 2001)) Therefore the present extraction system was
treated as fast reaction although further research is still needed to accurately describe it
3 Results and Discussion
31 Specific interfacial area
The rate of mass transfer between two phases depends on the interfacial area available For the
calculation of the interfacial area in plug flow it is assumed that the dispersed plugs have a cylindrical
body and hemispherical caps at the front and back When a continuous film is a present at the channel
wall the interfacial area can be calculated as follows with an error of less than 10(Raimondi et al
2014)
120572119901 =4119882119901(119871119875minus119908119901)+120587119882119901
2
1198711198801198621198681198632 (3)
where Luc is the unit cell length (one slug and one plug) and Wp and Lp represent the plug width and
length respectively The plug geometric parameters for each set of flow rates were obtained by averaging
results from 30 plugs with deviations between 425-710for film thickness and 533-952 for plug
and unit cell length
The effect of mixture velocity on interfacial area can be seen in Fig4 for equal flow rates of the two
phases from Qaq=QIL=3534 to 2121 mlh The interfacial area was found to increase slightly with
increasing Umix As the mixture velocity increases the plug formation frequency increases while shorter
plugs form which results in larger interfacial area values However the capillary diameter has a more
profound effect the interfacial area in the large channel is almost 3 times smaller than in the small one
7
for the same mixture velocity It has been suggested that the organic film can be ignored during mass
transfer at low mixture velocities (Ghaini et al 2010) However when ionic liquid is the continuous
phase the film (δfilmR = 01585-03022 where δfilm and R are film thickness and channel radius
respectively) is thicker than with conventional organic solvents (δfilm R = 00928-01295) and may affect
mass transfer
32 Distribution coefficients for Eu(III) extraction
To characterize the mass transfer process a number of parameters will be used The Eu(III) distribution
coefficient DEu is defined as the ratio of concentration of europium in the ionic liquid phase to the
concentration in the aqueous phase
119863119864119906 =119862119886119902119894119899119894minus119862119886119902
119890
119862119886119902119890 (4)
The Eu(III) distribution coefficients for the aqueous-ionic liquid system were measured at different nitric
acid concentrations (001 01 05 10 and 20M) In the experiments equal volumes of nitric acid
solution containing europium nitrate and of ionic liquid solution (02M CMPO-12M TBP[C4min][NTf2])
were mechanically shaken for 3 hours The initial loading of Eu(III) in the aqueous phase was 20 30 and
50 mgmL respectively After equilibrium the Eu(III) concentration was measured in the aqueous phase
in a UV-Vis spectrometer Fig5 illustrates the Eu(III) distribution coefficient (DEu) as a function of initial
nitric acid concentration (Caqini) Each equilibrium experiment was repeated 5 times The relative
deviation was quite large for the low Eu(III) loading (20mgmL) ranging between 369 and 2876
but decreased to 255 - 1418 at 50 mgmL loading where the absorption signal in the UV-Vis is
stronger and more stable than at lower loadings The Eu(III) concentration in the ionic liquid phase was
also measured with UV-Vis The amount after extraction was between 8965 to 10154 of the initial
Eu(III) loading It would be difficult to have better agreement because the IL cations the NO3-or the
impurities in the imidazolium-based ionic liquids also have absorption characteristics in the UV range
that can mask the Eu(III) signal (Billard et al 2011a)
As can be seen from Fig5 the distribution coefficient reduces with increasing Eu(III) loading which
means that the Eu(III) in the aqueous phase is more difficult to be distributed into the ionic liquid phase
However 50 mgmL concentration was chosen for the microchannel extraction experiments because of
the low concentration measurement errors Furthermore the distribution coefficient has its highest value
at 10M nitric acid concentration for all initial Eu(III) loadings which is in agreement with the results by
Rout et al (2011b) The distribution coefficients obtained when ionic liquid is used are by a factor of 10
higher to those achieved with the conventional TUREX solvent (02M CMPO-12M TBPn-DD) (Rout et
8
al 2011a)
33 Mass transfer in continuous extraction
The performance of a mass transfer unit is characterized by the mass transfer coefficient (KLa) The
driving force for mass transfer will vary along the length of the microchannel and a log mean
concentration difference (LMCD) can be used defined as
∆119871119872119862119863=(119862119886119902119894119899119894
119890 minus 119862119886119902119894119899119894) minus (119862119886119902119891119894119899119890 minus 119862119886119902119891119894119899)
ln(119862119886119902119894119899119894119890 minus 119862119886119902119894119899)(119862119886119902119891119894119899
119890 minus 119862119886119902119891119894119899)(5)
The mean value of the mass transfer flux can be written as
119873 = 119870119871∆119871119872119862119863 (6)
The mean value of the mass transfer flux is also equal to
=119928119938119954(119914119938119954119943119946119951minus119914119938119954119946119951)
119933120630119953(7)
By combining Eqn (6) and Eqn (7) and integrating from the initial (119862119886119902119894119899119894) to the final concentration
(119862119886119902119891119894119899) for time between 0 and the residence time τ the overall mass transfer coefficient is found
119870119871120572 =1
(1+1
119863119864119906
119876119886119902
119876119900119903119892)120591
ln (119862119886119902119891119894119899minus119862119886119902
119890
119862119886119902119894119899minus119862119886119902119890 ) (8)
The extraction efficiency Eeff refers to the ratio of the amount of species transferred to the maximum
amount transferable
119864119890119891119891 =Amount transferred
Maximum amount transferable=
119862119886119902119894119899minus119862119886119902119891119894119899
119862119886119902119894119899minus119862119886119902119890 (9)
The efficiency is a good indicator of the mass transfer performance of the contactor at various contact
times (Bapat and Tavlarides 1985 Dehkordi 2001) The extraction efficiency depends not only on the
overall volumetric mass transfer coefficient (KLa ) but also on the residence time (τ)
The overall volumetric mass transfer coefficients of the Eu(III) extraction in the 05 mm ID microchannel
calculated from Eqn (8) are shown in Fig6a as a function of residence time To obtain different
residence times (τ) the channel length was varied from 5 cm 15 cm to 25 cm at the same volumetric
flow rates of the two liquids Qaq= QIL=3534 mlhr The volumetric mass transfer coefficient was found to
decrease non-linearly with increasing residence time On average the mass transfer coefficient of τ=10s
(CL=5 cm) was 15 times higher than that of τ=30 s (CL=15 cm) under all nitric acid solutions while the
change between τ=30 s and τ=50 s (CL=25 cm) was small This suggests that the mass transfer at the inlet
of the channel contributes significantly to the overall mass transfer in the separation unit The nitric acid
9
concentration affects the mass transfer coefficient in a similar way that it affects the distribution
coefficient (Fig 5) The highest mass transfer was found at 10M nitric acid concentration followed by
the 05 and 20 M concentrations The lowest KLa were found for 01M nitric acid concentration
The effect of residence time on extraction efficiency can be seen in Fig6b In all cases the extraction
efficiency increases with residence time In the shortest channel (CL=5 cm and τ=10 s) the extraction
efficiency is relatively low (4355) despite the high mass transfer coefficients The highest Eeff was
found at 1M nitric acid concentration and at the longest residence time where it reaches 7150 of the
equilibrium value
34 Effect of mixture velocity on Eu(III) microfluidic extraction
The effect of mixture velocity on overall volumetric mass transfer coefficient was investigated in the
05mm ID microchannel (CL=15 cm) at varying nitric acid concentrations for equal volumetric flow
rates of the two phases ranging from Qaq=QIL=3534 to 2121 mlhr As can be seen in Fig7 for 1M nitric
acid concentration the mass transfer coefficient increases with increasing mixture velocity which means
the extraction system is mass transfer dominated The increase in the mass transfer coefficient is partly
attributed to the small increase in interfacial area (see Fig4) This contribution however is small for
example the area increases by 464 when the mass transfer coefficient rises by 54 for change in
velocity from 05 to 3 cms Mixture velocity affects mass transfer in plug flow via two mechanisms(a)
convection due to internal circulation in the plugs and slugs (b) molecular diffusion due to concentration
gradients adjacent to the interface (Kashid et al 2007 Dessimoz et al 2008) The increase in mixture
velocity increases the intensity of internal circulation and enhances convective mass transfer (Tsaoulidis
and Angeli 2015) The circulation also helps interface renewal that increases the concentration gradients
and therefore mass transfer close to the interface The mass transfer performance however does not
depend only on mixture velocity and as can be seen at nitric acid concentration different from 1M the
effect of mixture velocity on the mass transfer coefficient is less significant The extraction of Eu(III) is a
physical process combined with chemical reaction and depends on both mass transfer and intrinsic
reaction kinetics (Xu et al 2013)
To evaluate the role of film thickness on mass transfer van Baten and Krishna (2004) proposed different
correlations for mass transfer from the plug caps and the film in the plug flow regime
119870119871119888119886119901 = 2radic2
120587radic
119863119880119875
119889119888 (10)
119870119871119891119894119897119898 = 2radic119863
120587119905119891119894119897119898
119897119899(1 ∆frasl )
(1minus∆) Folt 01 (short contact) (11)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
5
High speed imaging was used to study the hydrodynamic characteristics of the two phase system (Fig 1)
A 60-Watt continuous arc lamp was used to volumetrically illuminate the microchannel from the back
and a diffuser plane was added between the backlight and the test section for uniform illumination To
minimize optical distortions an acrylic box filled with water was put around the channel Because of the
background illumination the interface appears as a shadow which is captured by a high speed camera
(Photron Fastcam-Ultima APX UK) with adjustable image recording frequency from 2000 to 8000Hz
depending on flowrates The camera was coupled with an air-immersion long working distance objective
lens with magnification M=3 to 10 depending on the channel dimension In addition a bright field
Particle Image Velocimetry technique was applied with the same optical set up to obtain the velocity
profiles within the aqueous plugs For the velocity measurements the aqueous phase was seeded with
3μm polystyrene particles and their shadow was recorded by the high speed camera (resolution
1024X1024 pix2) The Insight 4G (TSI instrument) software was used to pre-process and capture the
images while data analysis was carried out with an in-house MATLAB code A median filter was applied
to the images to eliminate any background noise The displacement of tracer particles between two
consecutive frames was calculated to obtain velocity vectors using a square domain discretization of 32 X
32 pixels with 50 overlap to satisfy the Nyquist sampling criterion(Dore et al 2012) with velocity
spatial resolution of 2672 μm times 2672 μm in the 05 mm channel The correlation peak position was
computed with Gaussian peak algorithm detection and the validation of the velocity vectors was based on
standard deviation and primary to secondary peak vectors Removed false vectors were replaced with the
median value of neighboring velocity vectors (Chinaud et al 2015)
22 Chemical mechanisms
The chemical structure of [C4min][NTf2] ionic liquid is shown in Fig3 The stoichiometry of
metal-solvate in the ionic liquid phase varies from 13 (Eu CMPO) at trace levels to 11 at higher Eu(III)
loadings It is determined by the slope analysis of logDEu against log[CMPO]org(Rout et al 2011b)
where species with overline exist in the ionic liquid phase only
Eu3+ + xCMPO + 3NO3minus harr Eu(NO3)3 ∙ (CMPO)x
(1)
However the equilibrium often involves ion exchange between the aqueous and the ionic liquid phases
Billard et al (2011a) found that the cation part of the ionic liquid C4mim+ was present into the aqueous
phase after extraction By dissolving C4mimCl into the aqueous phase it was shown that the presence of
C4mim+ reduced the extraction efficiency (Nakashima et al 2005) In some cases anion exchange was
also observed for example Tf2N- transferred to aqueous Htta solution when Eu(III) was extracted from
ionic liquid (Okamura et al 2012) However there is no clear evidence of anion exchange when ionic
liquid acts as diluent because Tf2N- is a weakly coordinating anion (Binnemans 2007) According to the
6
above the mechanism can be written as
Eu3+ + xCMPO + 3NO3minus + 3C4mim+ harr Eu(NO3)3 ∙ (CMPO)x
+ 3C4mim+ (2)
When ILs are used to recover Eu(III) in conjunction with neutral extractants the reaction takes place in
the ionic liquid phase and not in the aqueous phase as it happens with conventional solvents Very limited
research is available on the extraction kinetics of Eu(III) coupled with ionic liquid The separations of
certain rare earth metals are characterized by fast reaction but slow mass transfer using conventional
organic solutions (Sarkar et al 1980) When ionic liquids are used however this may not be the case
due to their unique ion exchange mechanisms Brigham (2013) investigated lanthanide extraction by
HDEHP in n-dodecane from DTPA and found that the reaction follows pseudo first- or second-order
kinetics The second order rate constant of Eu(III) extraction was about 104 M-1s-1 which falls into the
range of fast reactions (1 to 1010 M-1s-1(Caldin 2001)) Therefore the present extraction system was
treated as fast reaction although further research is still needed to accurately describe it
3 Results and Discussion
31 Specific interfacial area
The rate of mass transfer between two phases depends on the interfacial area available For the
calculation of the interfacial area in plug flow it is assumed that the dispersed plugs have a cylindrical
body and hemispherical caps at the front and back When a continuous film is a present at the channel
wall the interfacial area can be calculated as follows with an error of less than 10(Raimondi et al
2014)
120572119901 =4119882119901(119871119875minus119908119901)+120587119882119901
2
1198711198801198621198681198632 (3)
where Luc is the unit cell length (one slug and one plug) and Wp and Lp represent the plug width and
length respectively The plug geometric parameters for each set of flow rates were obtained by averaging
results from 30 plugs with deviations between 425-710for film thickness and 533-952 for plug
and unit cell length
The effect of mixture velocity on interfacial area can be seen in Fig4 for equal flow rates of the two
phases from Qaq=QIL=3534 to 2121 mlh The interfacial area was found to increase slightly with
increasing Umix As the mixture velocity increases the plug formation frequency increases while shorter
plugs form which results in larger interfacial area values However the capillary diameter has a more
profound effect the interfacial area in the large channel is almost 3 times smaller than in the small one
7
for the same mixture velocity It has been suggested that the organic film can be ignored during mass
transfer at low mixture velocities (Ghaini et al 2010) However when ionic liquid is the continuous
phase the film (δfilmR = 01585-03022 where δfilm and R are film thickness and channel radius
respectively) is thicker than with conventional organic solvents (δfilm R = 00928-01295) and may affect
mass transfer
32 Distribution coefficients for Eu(III) extraction
To characterize the mass transfer process a number of parameters will be used The Eu(III) distribution
coefficient DEu is defined as the ratio of concentration of europium in the ionic liquid phase to the
concentration in the aqueous phase
119863119864119906 =119862119886119902119894119899119894minus119862119886119902
119890
119862119886119902119890 (4)
The Eu(III) distribution coefficients for the aqueous-ionic liquid system were measured at different nitric
acid concentrations (001 01 05 10 and 20M) In the experiments equal volumes of nitric acid
solution containing europium nitrate and of ionic liquid solution (02M CMPO-12M TBP[C4min][NTf2])
were mechanically shaken for 3 hours The initial loading of Eu(III) in the aqueous phase was 20 30 and
50 mgmL respectively After equilibrium the Eu(III) concentration was measured in the aqueous phase
in a UV-Vis spectrometer Fig5 illustrates the Eu(III) distribution coefficient (DEu) as a function of initial
nitric acid concentration (Caqini) Each equilibrium experiment was repeated 5 times The relative
deviation was quite large for the low Eu(III) loading (20mgmL) ranging between 369 and 2876
but decreased to 255 - 1418 at 50 mgmL loading where the absorption signal in the UV-Vis is
stronger and more stable than at lower loadings The Eu(III) concentration in the ionic liquid phase was
also measured with UV-Vis The amount after extraction was between 8965 to 10154 of the initial
Eu(III) loading It would be difficult to have better agreement because the IL cations the NO3-or the
impurities in the imidazolium-based ionic liquids also have absorption characteristics in the UV range
that can mask the Eu(III) signal (Billard et al 2011a)
As can be seen from Fig5 the distribution coefficient reduces with increasing Eu(III) loading which
means that the Eu(III) in the aqueous phase is more difficult to be distributed into the ionic liquid phase
However 50 mgmL concentration was chosen for the microchannel extraction experiments because of
the low concentration measurement errors Furthermore the distribution coefficient has its highest value
at 10M nitric acid concentration for all initial Eu(III) loadings which is in agreement with the results by
Rout et al (2011b) The distribution coefficients obtained when ionic liquid is used are by a factor of 10
higher to those achieved with the conventional TUREX solvent (02M CMPO-12M TBPn-DD) (Rout et
8
al 2011a)
33 Mass transfer in continuous extraction
The performance of a mass transfer unit is characterized by the mass transfer coefficient (KLa) The
driving force for mass transfer will vary along the length of the microchannel and a log mean
concentration difference (LMCD) can be used defined as
∆119871119872119862119863=(119862119886119902119894119899119894
119890 minus 119862119886119902119894119899119894) minus (119862119886119902119891119894119899119890 minus 119862119886119902119891119894119899)
ln(119862119886119902119894119899119894119890 minus 119862119886119902119894119899)(119862119886119902119891119894119899
119890 minus 119862119886119902119891119894119899)(5)
The mean value of the mass transfer flux can be written as
119873 = 119870119871∆119871119872119862119863 (6)
The mean value of the mass transfer flux is also equal to
=119928119938119954(119914119938119954119943119946119951minus119914119938119954119946119951)
119933120630119953(7)
By combining Eqn (6) and Eqn (7) and integrating from the initial (119862119886119902119894119899119894) to the final concentration
(119862119886119902119891119894119899) for time between 0 and the residence time τ the overall mass transfer coefficient is found
119870119871120572 =1
(1+1
119863119864119906
119876119886119902
119876119900119903119892)120591
ln (119862119886119902119891119894119899minus119862119886119902
119890
119862119886119902119894119899minus119862119886119902119890 ) (8)
The extraction efficiency Eeff refers to the ratio of the amount of species transferred to the maximum
amount transferable
119864119890119891119891 =Amount transferred
Maximum amount transferable=
119862119886119902119894119899minus119862119886119902119891119894119899
119862119886119902119894119899minus119862119886119902119890 (9)
The efficiency is a good indicator of the mass transfer performance of the contactor at various contact
times (Bapat and Tavlarides 1985 Dehkordi 2001) The extraction efficiency depends not only on the
overall volumetric mass transfer coefficient (KLa ) but also on the residence time (τ)
The overall volumetric mass transfer coefficients of the Eu(III) extraction in the 05 mm ID microchannel
calculated from Eqn (8) are shown in Fig6a as a function of residence time To obtain different
residence times (τ) the channel length was varied from 5 cm 15 cm to 25 cm at the same volumetric
flow rates of the two liquids Qaq= QIL=3534 mlhr The volumetric mass transfer coefficient was found to
decrease non-linearly with increasing residence time On average the mass transfer coefficient of τ=10s
(CL=5 cm) was 15 times higher than that of τ=30 s (CL=15 cm) under all nitric acid solutions while the
change between τ=30 s and τ=50 s (CL=25 cm) was small This suggests that the mass transfer at the inlet
of the channel contributes significantly to the overall mass transfer in the separation unit The nitric acid
9
concentration affects the mass transfer coefficient in a similar way that it affects the distribution
coefficient (Fig 5) The highest mass transfer was found at 10M nitric acid concentration followed by
the 05 and 20 M concentrations The lowest KLa were found for 01M nitric acid concentration
The effect of residence time on extraction efficiency can be seen in Fig6b In all cases the extraction
efficiency increases with residence time In the shortest channel (CL=5 cm and τ=10 s) the extraction
efficiency is relatively low (4355) despite the high mass transfer coefficients The highest Eeff was
found at 1M nitric acid concentration and at the longest residence time where it reaches 7150 of the
equilibrium value
34 Effect of mixture velocity on Eu(III) microfluidic extraction
The effect of mixture velocity on overall volumetric mass transfer coefficient was investigated in the
05mm ID microchannel (CL=15 cm) at varying nitric acid concentrations for equal volumetric flow
rates of the two phases ranging from Qaq=QIL=3534 to 2121 mlhr As can be seen in Fig7 for 1M nitric
acid concentration the mass transfer coefficient increases with increasing mixture velocity which means
the extraction system is mass transfer dominated The increase in the mass transfer coefficient is partly
attributed to the small increase in interfacial area (see Fig4) This contribution however is small for
example the area increases by 464 when the mass transfer coefficient rises by 54 for change in
velocity from 05 to 3 cms Mixture velocity affects mass transfer in plug flow via two mechanisms(a)
convection due to internal circulation in the plugs and slugs (b) molecular diffusion due to concentration
gradients adjacent to the interface (Kashid et al 2007 Dessimoz et al 2008) The increase in mixture
velocity increases the intensity of internal circulation and enhances convective mass transfer (Tsaoulidis
and Angeli 2015) The circulation also helps interface renewal that increases the concentration gradients
and therefore mass transfer close to the interface The mass transfer performance however does not
depend only on mixture velocity and as can be seen at nitric acid concentration different from 1M the
effect of mixture velocity on the mass transfer coefficient is less significant The extraction of Eu(III) is a
physical process combined with chemical reaction and depends on both mass transfer and intrinsic
reaction kinetics (Xu et al 2013)
To evaluate the role of film thickness on mass transfer van Baten and Krishna (2004) proposed different
correlations for mass transfer from the plug caps and the film in the plug flow regime
119870119871119888119886119901 = 2radic2
120587radic
119863119880119875
119889119888 (10)
119870119871119891119894119897119898 = 2radic119863
120587119905119891119894119897119898
119897119899(1 ∆frasl )
(1minus∆) Folt 01 (short contact) (11)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
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Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
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17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
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Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
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Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
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Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
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Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
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Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
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Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
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Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
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Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
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Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
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Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
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Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
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capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
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liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
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applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
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Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
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21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
6
above the mechanism can be written as
Eu3+ + xCMPO + 3NO3minus + 3C4mim+ harr Eu(NO3)3 ∙ (CMPO)x
+ 3C4mim+ (2)
When ILs are used to recover Eu(III) in conjunction with neutral extractants the reaction takes place in
the ionic liquid phase and not in the aqueous phase as it happens with conventional solvents Very limited
research is available on the extraction kinetics of Eu(III) coupled with ionic liquid The separations of
certain rare earth metals are characterized by fast reaction but slow mass transfer using conventional
organic solutions (Sarkar et al 1980) When ionic liquids are used however this may not be the case
due to their unique ion exchange mechanisms Brigham (2013) investigated lanthanide extraction by
HDEHP in n-dodecane from DTPA and found that the reaction follows pseudo first- or second-order
kinetics The second order rate constant of Eu(III) extraction was about 104 M-1s-1 which falls into the
range of fast reactions (1 to 1010 M-1s-1(Caldin 2001)) Therefore the present extraction system was
treated as fast reaction although further research is still needed to accurately describe it
3 Results and Discussion
31 Specific interfacial area
The rate of mass transfer between two phases depends on the interfacial area available For the
calculation of the interfacial area in plug flow it is assumed that the dispersed plugs have a cylindrical
body and hemispherical caps at the front and back When a continuous film is a present at the channel
wall the interfacial area can be calculated as follows with an error of less than 10(Raimondi et al
2014)
120572119901 =4119882119901(119871119875minus119908119901)+120587119882119901
2
1198711198801198621198681198632 (3)
where Luc is the unit cell length (one slug and one plug) and Wp and Lp represent the plug width and
length respectively The plug geometric parameters for each set of flow rates were obtained by averaging
results from 30 plugs with deviations between 425-710for film thickness and 533-952 for plug
and unit cell length
The effect of mixture velocity on interfacial area can be seen in Fig4 for equal flow rates of the two
phases from Qaq=QIL=3534 to 2121 mlh The interfacial area was found to increase slightly with
increasing Umix As the mixture velocity increases the plug formation frequency increases while shorter
plugs form which results in larger interfacial area values However the capillary diameter has a more
profound effect the interfacial area in the large channel is almost 3 times smaller than in the small one
7
for the same mixture velocity It has been suggested that the organic film can be ignored during mass
transfer at low mixture velocities (Ghaini et al 2010) However when ionic liquid is the continuous
phase the film (δfilmR = 01585-03022 where δfilm and R are film thickness and channel radius
respectively) is thicker than with conventional organic solvents (δfilm R = 00928-01295) and may affect
mass transfer
32 Distribution coefficients for Eu(III) extraction
To characterize the mass transfer process a number of parameters will be used The Eu(III) distribution
coefficient DEu is defined as the ratio of concentration of europium in the ionic liquid phase to the
concentration in the aqueous phase
119863119864119906 =119862119886119902119894119899119894minus119862119886119902
119890
119862119886119902119890 (4)
The Eu(III) distribution coefficients for the aqueous-ionic liquid system were measured at different nitric
acid concentrations (001 01 05 10 and 20M) In the experiments equal volumes of nitric acid
solution containing europium nitrate and of ionic liquid solution (02M CMPO-12M TBP[C4min][NTf2])
were mechanically shaken for 3 hours The initial loading of Eu(III) in the aqueous phase was 20 30 and
50 mgmL respectively After equilibrium the Eu(III) concentration was measured in the aqueous phase
in a UV-Vis spectrometer Fig5 illustrates the Eu(III) distribution coefficient (DEu) as a function of initial
nitric acid concentration (Caqini) Each equilibrium experiment was repeated 5 times The relative
deviation was quite large for the low Eu(III) loading (20mgmL) ranging between 369 and 2876
but decreased to 255 - 1418 at 50 mgmL loading where the absorption signal in the UV-Vis is
stronger and more stable than at lower loadings The Eu(III) concentration in the ionic liquid phase was
also measured with UV-Vis The amount after extraction was between 8965 to 10154 of the initial
Eu(III) loading It would be difficult to have better agreement because the IL cations the NO3-or the
impurities in the imidazolium-based ionic liquids also have absorption characteristics in the UV range
that can mask the Eu(III) signal (Billard et al 2011a)
As can be seen from Fig5 the distribution coefficient reduces with increasing Eu(III) loading which
means that the Eu(III) in the aqueous phase is more difficult to be distributed into the ionic liquid phase
However 50 mgmL concentration was chosen for the microchannel extraction experiments because of
the low concentration measurement errors Furthermore the distribution coefficient has its highest value
at 10M nitric acid concentration for all initial Eu(III) loadings which is in agreement with the results by
Rout et al (2011b) The distribution coefficients obtained when ionic liquid is used are by a factor of 10
higher to those achieved with the conventional TUREX solvent (02M CMPO-12M TBPn-DD) (Rout et
8
al 2011a)
33 Mass transfer in continuous extraction
The performance of a mass transfer unit is characterized by the mass transfer coefficient (KLa) The
driving force for mass transfer will vary along the length of the microchannel and a log mean
concentration difference (LMCD) can be used defined as
∆119871119872119862119863=(119862119886119902119894119899119894
119890 minus 119862119886119902119894119899119894) minus (119862119886119902119891119894119899119890 minus 119862119886119902119891119894119899)
ln(119862119886119902119894119899119894119890 minus 119862119886119902119894119899)(119862119886119902119891119894119899
119890 minus 119862119886119902119891119894119899)(5)
The mean value of the mass transfer flux can be written as
119873 = 119870119871∆119871119872119862119863 (6)
The mean value of the mass transfer flux is also equal to
=119928119938119954(119914119938119954119943119946119951minus119914119938119954119946119951)
119933120630119953(7)
By combining Eqn (6) and Eqn (7) and integrating from the initial (119862119886119902119894119899119894) to the final concentration
(119862119886119902119891119894119899) for time between 0 and the residence time τ the overall mass transfer coefficient is found
119870119871120572 =1
(1+1
119863119864119906
119876119886119902
119876119900119903119892)120591
ln (119862119886119902119891119894119899minus119862119886119902
119890
119862119886119902119894119899minus119862119886119902119890 ) (8)
The extraction efficiency Eeff refers to the ratio of the amount of species transferred to the maximum
amount transferable
119864119890119891119891 =Amount transferred
Maximum amount transferable=
119862119886119902119894119899minus119862119886119902119891119894119899
119862119886119902119894119899minus119862119886119902119890 (9)
The efficiency is a good indicator of the mass transfer performance of the contactor at various contact
times (Bapat and Tavlarides 1985 Dehkordi 2001) The extraction efficiency depends not only on the
overall volumetric mass transfer coefficient (KLa ) but also on the residence time (τ)
The overall volumetric mass transfer coefficients of the Eu(III) extraction in the 05 mm ID microchannel
calculated from Eqn (8) are shown in Fig6a as a function of residence time To obtain different
residence times (τ) the channel length was varied from 5 cm 15 cm to 25 cm at the same volumetric
flow rates of the two liquids Qaq= QIL=3534 mlhr The volumetric mass transfer coefficient was found to
decrease non-linearly with increasing residence time On average the mass transfer coefficient of τ=10s
(CL=5 cm) was 15 times higher than that of τ=30 s (CL=15 cm) under all nitric acid solutions while the
change between τ=30 s and τ=50 s (CL=25 cm) was small This suggests that the mass transfer at the inlet
of the channel contributes significantly to the overall mass transfer in the separation unit The nitric acid
9
concentration affects the mass transfer coefficient in a similar way that it affects the distribution
coefficient (Fig 5) The highest mass transfer was found at 10M nitric acid concentration followed by
the 05 and 20 M concentrations The lowest KLa were found for 01M nitric acid concentration
The effect of residence time on extraction efficiency can be seen in Fig6b In all cases the extraction
efficiency increases with residence time In the shortest channel (CL=5 cm and τ=10 s) the extraction
efficiency is relatively low (4355) despite the high mass transfer coefficients The highest Eeff was
found at 1M nitric acid concentration and at the longest residence time where it reaches 7150 of the
equilibrium value
34 Effect of mixture velocity on Eu(III) microfluidic extraction
The effect of mixture velocity on overall volumetric mass transfer coefficient was investigated in the
05mm ID microchannel (CL=15 cm) at varying nitric acid concentrations for equal volumetric flow
rates of the two phases ranging from Qaq=QIL=3534 to 2121 mlhr As can be seen in Fig7 for 1M nitric
acid concentration the mass transfer coefficient increases with increasing mixture velocity which means
the extraction system is mass transfer dominated The increase in the mass transfer coefficient is partly
attributed to the small increase in interfacial area (see Fig4) This contribution however is small for
example the area increases by 464 when the mass transfer coefficient rises by 54 for change in
velocity from 05 to 3 cms Mixture velocity affects mass transfer in plug flow via two mechanisms(a)
convection due to internal circulation in the plugs and slugs (b) molecular diffusion due to concentration
gradients adjacent to the interface (Kashid et al 2007 Dessimoz et al 2008) The increase in mixture
velocity increases the intensity of internal circulation and enhances convective mass transfer (Tsaoulidis
and Angeli 2015) The circulation also helps interface renewal that increases the concentration gradients
and therefore mass transfer close to the interface The mass transfer performance however does not
depend only on mixture velocity and as can be seen at nitric acid concentration different from 1M the
effect of mixture velocity on the mass transfer coefficient is less significant The extraction of Eu(III) is a
physical process combined with chemical reaction and depends on both mass transfer and intrinsic
reaction kinetics (Xu et al 2013)
To evaluate the role of film thickness on mass transfer van Baten and Krishna (2004) proposed different
correlations for mass transfer from the plug caps and the film in the plug flow regime
119870119871119888119886119901 = 2radic2
120587radic
119863119880119875
119889119888 (10)
119870119871119891119894119897119898 = 2radic119863
120587119905119891119894119897119898
119897119899(1 ∆frasl )
(1minus∆) Folt 01 (short contact) (11)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
7
for the same mixture velocity It has been suggested that the organic film can be ignored during mass
transfer at low mixture velocities (Ghaini et al 2010) However when ionic liquid is the continuous
phase the film (δfilmR = 01585-03022 where δfilm and R are film thickness and channel radius
respectively) is thicker than with conventional organic solvents (δfilm R = 00928-01295) and may affect
mass transfer
32 Distribution coefficients for Eu(III) extraction
To characterize the mass transfer process a number of parameters will be used The Eu(III) distribution
coefficient DEu is defined as the ratio of concentration of europium in the ionic liquid phase to the
concentration in the aqueous phase
119863119864119906 =119862119886119902119894119899119894minus119862119886119902
119890
119862119886119902119890 (4)
The Eu(III) distribution coefficients for the aqueous-ionic liquid system were measured at different nitric
acid concentrations (001 01 05 10 and 20M) In the experiments equal volumes of nitric acid
solution containing europium nitrate and of ionic liquid solution (02M CMPO-12M TBP[C4min][NTf2])
were mechanically shaken for 3 hours The initial loading of Eu(III) in the aqueous phase was 20 30 and
50 mgmL respectively After equilibrium the Eu(III) concentration was measured in the aqueous phase
in a UV-Vis spectrometer Fig5 illustrates the Eu(III) distribution coefficient (DEu) as a function of initial
nitric acid concentration (Caqini) Each equilibrium experiment was repeated 5 times The relative
deviation was quite large for the low Eu(III) loading (20mgmL) ranging between 369 and 2876
but decreased to 255 - 1418 at 50 mgmL loading where the absorption signal in the UV-Vis is
stronger and more stable than at lower loadings The Eu(III) concentration in the ionic liquid phase was
also measured with UV-Vis The amount after extraction was between 8965 to 10154 of the initial
Eu(III) loading It would be difficult to have better agreement because the IL cations the NO3-or the
impurities in the imidazolium-based ionic liquids also have absorption characteristics in the UV range
that can mask the Eu(III) signal (Billard et al 2011a)
As can be seen from Fig5 the distribution coefficient reduces with increasing Eu(III) loading which
means that the Eu(III) in the aqueous phase is more difficult to be distributed into the ionic liquid phase
However 50 mgmL concentration was chosen for the microchannel extraction experiments because of
the low concentration measurement errors Furthermore the distribution coefficient has its highest value
at 10M nitric acid concentration for all initial Eu(III) loadings which is in agreement with the results by
Rout et al (2011b) The distribution coefficients obtained when ionic liquid is used are by a factor of 10
higher to those achieved with the conventional TUREX solvent (02M CMPO-12M TBPn-DD) (Rout et
8
al 2011a)
33 Mass transfer in continuous extraction
The performance of a mass transfer unit is characterized by the mass transfer coefficient (KLa) The
driving force for mass transfer will vary along the length of the microchannel and a log mean
concentration difference (LMCD) can be used defined as
∆119871119872119862119863=(119862119886119902119894119899119894
119890 minus 119862119886119902119894119899119894) minus (119862119886119902119891119894119899119890 minus 119862119886119902119891119894119899)
ln(119862119886119902119894119899119894119890 minus 119862119886119902119894119899)(119862119886119902119891119894119899
119890 minus 119862119886119902119891119894119899)(5)
The mean value of the mass transfer flux can be written as
119873 = 119870119871∆119871119872119862119863 (6)
The mean value of the mass transfer flux is also equal to
=119928119938119954(119914119938119954119943119946119951minus119914119938119954119946119951)
119933120630119953(7)
By combining Eqn (6) and Eqn (7) and integrating from the initial (119862119886119902119894119899119894) to the final concentration
(119862119886119902119891119894119899) for time between 0 and the residence time τ the overall mass transfer coefficient is found
119870119871120572 =1
(1+1
119863119864119906
119876119886119902
119876119900119903119892)120591
ln (119862119886119902119891119894119899minus119862119886119902
119890
119862119886119902119894119899minus119862119886119902119890 ) (8)
The extraction efficiency Eeff refers to the ratio of the amount of species transferred to the maximum
amount transferable
119864119890119891119891 =Amount transferred
Maximum amount transferable=
119862119886119902119894119899minus119862119886119902119891119894119899
119862119886119902119894119899minus119862119886119902119890 (9)
The efficiency is a good indicator of the mass transfer performance of the contactor at various contact
times (Bapat and Tavlarides 1985 Dehkordi 2001) The extraction efficiency depends not only on the
overall volumetric mass transfer coefficient (KLa ) but also on the residence time (τ)
The overall volumetric mass transfer coefficients of the Eu(III) extraction in the 05 mm ID microchannel
calculated from Eqn (8) are shown in Fig6a as a function of residence time To obtain different
residence times (τ) the channel length was varied from 5 cm 15 cm to 25 cm at the same volumetric
flow rates of the two liquids Qaq= QIL=3534 mlhr The volumetric mass transfer coefficient was found to
decrease non-linearly with increasing residence time On average the mass transfer coefficient of τ=10s
(CL=5 cm) was 15 times higher than that of τ=30 s (CL=15 cm) under all nitric acid solutions while the
change between τ=30 s and τ=50 s (CL=25 cm) was small This suggests that the mass transfer at the inlet
of the channel contributes significantly to the overall mass transfer in the separation unit The nitric acid
9
concentration affects the mass transfer coefficient in a similar way that it affects the distribution
coefficient (Fig 5) The highest mass transfer was found at 10M nitric acid concentration followed by
the 05 and 20 M concentrations The lowest KLa were found for 01M nitric acid concentration
The effect of residence time on extraction efficiency can be seen in Fig6b In all cases the extraction
efficiency increases with residence time In the shortest channel (CL=5 cm and τ=10 s) the extraction
efficiency is relatively low (4355) despite the high mass transfer coefficients The highest Eeff was
found at 1M nitric acid concentration and at the longest residence time where it reaches 7150 of the
equilibrium value
34 Effect of mixture velocity on Eu(III) microfluidic extraction
The effect of mixture velocity on overall volumetric mass transfer coefficient was investigated in the
05mm ID microchannel (CL=15 cm) at varying nitric acid concentrations for equal volumetric flow
rates of the two phases ranging from Qaq=QIL=3534 to 2121 mlhr As can be seen in Fig7 for 1M nitric
acid concentration the mass transfer coefficient increases with increasing mixture velocity which means
the extraction system is mass transfer dominated The increase in the mass transfer coefficient is partly
attributed to the small increase in interfacial area (see Fig4) This contribution however is small for
example the area increases by 464 when the mass transfer coefficient rises by 54 for change in
velocity from 05 to 3 cms Mixture velocity affects mass transfer in plug flow via two mechanisms(a)
convection due to internal circulation in the plugs and slugs (b) molecular diffusion due to concentration
gradients adjacent to the interface (Kashid et al 2007 Dessimoz et al 2008) The increase in mixture
velocity increases the intensity of internal circulation and enhances convective mass transfer (Tsaoulidis
and Angeli 2015) The circulation also helps interface renewal that increases the concentration gradients
and therefore mass transfer close to the interface The mass transfer performance however does not
depend only on mixture velocity and as can be seen at nitric acid concentration different from 1M the
effect of mixture velocity on the mass transfer coefficient is less significant The extraction of Eu(III) is a
physical process combined with chemical reaction and depends on both mass transfer and intrinsic
reaction kinetics (Xu et al 2013)
To evaluate the role of film thickness on mass transfer van Baten and Krishna (2004) proposed different
correlations for mass transfer from the plug caps and the film in the plug flow regime
119870119871119888119886119901 = 2radic2
120587radic
119863119880119875
119889119888 (10)
119870119871119891119894119897119898 = 2radic119863
120587119905119891119894119897119898
119897119899(1 ∆frasl )
(1minus∆) Folt 01 (short contact) (11)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
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Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
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Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
8
al 2011a)
33 Mass transfer in continuous extraction
The performance of a mass transfer unit is characterized by the mass transfer coefficient (KLa) The
driving force for mass transfer will vary along the length of the microchannel and a log mean
concentration difference (LMCD) can be used defined as
∆119871119872119862119863=(119862119886119902119894119899119894
119890 minus 119862119886119902119894119899119894) minus (119862119886119902119891119894119899119890 minus 119862119886119902119891119894119899)
ln(119862119886119902119894119899119894119890 minus 119862119886119902119894119899)(119862119886119902119891119894119899
119890 minus 119862119886119902119891119894119899)(5)
The mean value of the mass transfer flux can be written as
119873 = 119870119871∆119871119872119862119863 (6)
The mean value of the mass transfer flux is also equal to
=119928119938119954(119914119938119954119943119946119951minus119914119938119954119946119951)
119933120630119953(7)
By combining Eqn (6) and Eqn (7) and integrating from the initial (119862119886119902119894119899119894) to the final concentration
(119862119886119902119891119894119899) for time between 0 and the residence time τ the overall mass transfer coefficient is found
119870119871120572 =1
(1+1
119863119864119906
119876119886119902
119876119900119903119892)120591
ln (119862119886119902119891119894119899minus119862119886119902
119890
119862119886119902119894119899minus119862119886119902119890 ) (8)
The extraction efficiency Eeff refers to the ratio of the amount of species transferred to the maximum
amount transferable
119864119890119891119891 =Amount transferred
Maximum amount transferable=
119862119886119902119894119899minus119862119886119902119891119894119899
119862119886119902119894119899minus119862119886119902119890 (9)
The efficiency is a good indicator of the mass transfer performance of the contactor at various contact
times (Bapat and Tavlarides 1985 Dehkordi 2001) The extraction efficiency depends not only on the
overall volumetric mass transfer coefficient (KLa ) but also on the residence time (τ)
The overall volumetric mass transfer coefficients of the Eu(III) extraction in the 05 mm ID microchannel
calculated from Eqn (8) are shown in Fig6a as a function of residence time To obtain different
residence times (τ) the channel length was varied from 5 cm 15 cm to 25 cm at the same volumetric
flow rates of the two liquids Qaq= QIL=3534 mlhr The volumetric mass transfer coefficient was found to
decrease non-linearly with increasing residence time On average the mass transfer coefficient of τ=10s
(CL=5 cm) was 15 times higher than that of τ=30 s (CL=15 cm) under all nitric acid solutions while the
change between τ=30 s and τ=50 s (CL=25 cm) was small This suggests that the mass transfer at the inlet
of the channel contributes significantly to the overall mass transfer in the separation unit The nitric acid
9
concentration affects the mass transfer coefficient in a similar way that it affects the distribution
coefficient (Fig 5) The highest mass transfer was found at 10M nitric acid concentration followed by
the 05 and 20 M concentrations The lowest KLa were found for 01M nitric acid concentration
The effect of residence time on extraction efficiency can be seen in Fig6b In all cases the extraction
efficiency increases with residence time In the shortest channel (CL=5 cm and τ=10 s) the extraction
efficiency is relatively low (4355) despite the high mass transfer coefficients The highest Eeff was
found at 1M nitric acid concentration and at the longest residence time where it reaches 7150 of the
equilibrium value
34 Effect of mixture velocity on Eu(III) microfluidic extraction
The effect of mixture velocity on overall volumetric mass transfer coefficient was investigated in the
05mm ID microchannel (CL=15 cm) at varying nitric acid concentrations for equal volumetric flow
rates of the two phases ranging from Qaq=QIL=3534 to 2121 mlhr As can be seen in Fig7 for 1M nitric
acid concentration the mass transfer coefficient increases with increasing mixture velocity which means
the extraction system is mass transfer dominated The increase in the mass transfer coefficient is partly
attributed to the small increase in interfacial area (see Fig4) This contribution however is small for
example the area increases by 464 when the mass transfer coefficient rises by 54 for change in
velocity from 05 to 3 cms Mixture velocity affects mass transfer in plug flow via two mechanisms(a)
convection due to internal circulation in the plugs and slugs (b) molecular diffusion due to concentration
gradients adjacent to the interface (Kashid et al 2007 Dessimoz et al 2008) The increase in mixture
velocity increases the intensity of internal circulation and enhances convective mass transfer (Tsaoulidis
and Angeli 2015) The circulation also helps interface renewal that increases the concentration gradients
and therefore mass transfer close to the interface The mass transfer performance however does not
depend only on mixture velocity and as can be seen at nitric acid concentration different from 1M the
effect of mixture velocity on the mass transfer coefficient is less significant The extraction of Eu(III) is a
physical process combined with chemical reaction and depends on both mass transfer and intrinsic
reaction kinetics (Xu et al 2013)
To evaluate the role of film thickness on mass transfer van Baten and Krishna (2004) proposed different
correlations for mass transfer from the plug caps and the film in the plug flow regime
119870119871119888119886119901 = 2radic2
120587radic
119863119880119875
119889119888 (10)
119870119871119891119894119897119898 = 2radic119863
120587119905119891119894119897119898
119897119899(1 ∆frasl )
(1minus∆) Folt 01 (short contact) (11)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
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Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
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De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
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Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
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Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
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Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
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Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
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Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
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Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
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Chemistry 290 215-219
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Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
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20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
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Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
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281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
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Journal na-na
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Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
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applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
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21
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cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
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T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
9
concentration affects the mass transfer coefficient in a similar way that it affects the distribution
coefficient (Fig 5) The highest mass transfer was found at 10M nitric acid concentration followed by
the 05 and 20 M concentrations The lowest KLa were found for 01M nitric acid concentration
The effect of residence time on extraction efficiency can be seen in Fig6b In all cases the extraction
efficiency increases with residence time In the shortest channel (CL=5 cm and τ=10 s) the extraction
efficiency is relatively low (4355) despite the high mass transfer coefficients The highest Eeff was
found at 1M nitric acid concentration and at the longest residence time where it reaches 7150 of the
equilibrium value
34 Effect of mixture velocity on Eu(III) microfluidic extraction
The effect of mixture velocity on overall volumetric mass transfer coefficient was investigated in the
05mm ID microchannel (CL=15 cm) at varying nitric acid concentrations for equal volumetric flow
rates of the two phases ranging from Qaq=QIL=3534 to 2121 mlhr As can be seen in Fig7 for 1M nitric
acid concentration the mass transfer coefficient increases with increasing mixture velocity which means
the extraction system is mass transfer dominated The increase in the mass transfer coefficient is partly
attributed to the small increase in interfacial area (see Fig4) This contribution however is small for
example the area increases by 464 when the mass transfer coefficient rises by 54 for change in
velocity from 05 to 3 cms Mixture velocity affects mass transfer in plug flow via two mechanisms(a)
convection due to internal circulation in the plugs and slugs (b) molecular diffusion due to concentration
gradients adjacent to the interface (Kashid et al 2007 Dessimoz et al 2008) The increase in mixture
velocity increases the intensity of internal circulation and enhances convective mass transfer (Tsaoulidis
and Angeli 2015) The circulation also helps interface renewal that increases the concentration gradients
and therefore mass transfer close to the interface The mass transfer performance however does not
depend only on mixture velocity and as can be seen at nitric acid concentration different from 1M the
effect of mixture velocity on the mass transfer coefficient is less significant The extraction of Eu(III) is a
physical process combined with chemical reaction and depends on both mass transfer and intrinsic
reaction kinetics (Xu et al 2013)
To evaluate the role of film thickness on mass transfer van Baten and Krishna (2004) proposed different
correlations for mass transfer from the plug caps and the film in the plug flow regime
119870119871119888119886119901 = 2radic2
120587radic
119863119880119875
119889119888 (10)
119870119871119891119894119897119898 = 2radic119863
120587119905119891119894119897119898
119897119899(1 ∆frasl )
(1minus∆) Folt 01 (short contact) (11)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
10
119870119871119891119894119897119898 = 341119863
120575119891119894119897119898 Fogt 01 (long contact) (12)
119870119871120572 = 119870119871119888119886119901120572119888119886119901 + 119870119871119891119894119897119898120572119891119894119897119898 (13)
where the Fourier number (Fo) is defined as Fo=Dtfilm δfilm2 and ∆ is a dimensionless parameter based on
Fo The plug velocity Up is obtained based on the plug displacement from the high speed imaging The
contact time of the liquid film tfilm =Lfilm (Up + Ufilm) is calculated under the assumption that the film
velocity is nearly negligible in the microchannel The mass transfer via the film can be evaluated
depending on the value of the Fourier number (Fo) where Folt 01 and Fogt 01 for short and long
contact time respectively The aqueous plug in the present work shows long film contact times as Fo
ranges between 0486 and 1235 The Eu(III) KLfilm in the 02 mm ID channel was found to decrease from
4702 to 3353 times 10-7 ms-1 when Umix increased from 001 to 006 ms and KLcap increased from 1151 to
2985 times 10-5 ms-1 under the same operation conditions These results show that 99 Eu(III) is extracted
via the cap regions and the film region has a minor effect on the overall mass transfer It explains why
high KLa occurs at larger Umix where plug formation frequency increases and shorter plugs form which
would result in increased cap regions that enhance mass transfer At Umixgt004 ms where Fogt08 and
Δasymp0 (van Baten and Krishna (2004)) the ionic liquid film approaches saturation and its contribution to
the overall mass transfer becomes insignificant
The Eu(III) extraction efficiency is shown in Fig 8 for the 05 mm ID microchannel (CL=15 cm) The
extraction efficiency increases with increasing residence time (decreasing mixture velocity) The highest
extraction efficiencies are obtained for 1M nitric acid concentration similar to distribution coefficients
(see Fig 5) Although the mass transfer coefficient at Umix=3 cms has the highest values the
corresponding extraction efficiencies are only 3624 to 5813 of the equilibrium value due to the short
residence times (τ=5s)
35 Effect of capillary size on Eu(III) extraction
The effect of channel size on overall volumetric mass transfer coefficient is shown in Fig9 for 02 and
05 mm ID capillaries as a function of mixture velocity at the same channel length (CL=25 cm) 1M nitric
acid was used as aqueous phase and equal flow rates of the both phases were used varying from 0065 to
1414mlh Generally KLa are higher in the small channel because of the large interfacial area compared
to the 05 mm channel As depicted in Fig4 the average interfacial area increases from 3600 m2m3 to
8250 m2m3 when the capillary internal diameter reduces from 05mm to 02mm The difference between
the mass transfer coefficients increases with mixture velocity For example at Umix=1 cms the difference
is about 105 of the 05 mm channel KLa but increases to 214 at Umix=3 cms The increased surface
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
11
renewal rate and recirculation intensity caused by higher plug velocities in the small channel are
considered to be responsible for the difference In fact the plug velocity is always higher than the
mixture velocity in the liquid-liquid plug flow regime due to the existence of a nearly stagnant ionic film
surrounding the aqueous phase plug The non-dimensional film thickness (δfilmR) in the 02 mm ID
channel was found to be 847-3292 larger than in the 05 mm ID channel from the imaging
experiments depending on the mixture velocity Therefore the enclosed plug moves slightly faster in the
small channel This is also confirmed by the imaging experiments which showed that plugs in the 02
mm ID channel moved594- 1774 faster compared to the large channel
36 Effect of recirculation intensity on Eu(III) microfluidic extraction
The convective mass transfer inside the plugs is strongly affected by the recirculation patterns which are
caused by the shear between the continuous phase and the plug axis To obtain the recirculation patterns
for each set of conditions the instantaneous velocity profiles of 30 plugs were averaged with a deviation
of 435-999 The average plug velocity was then calculated by integrating the laminar velocity profiles
of the averaged velocity field along the plug length The recirculation pattern was finally obtained by
subtracting the average velocity from the local velocities in the plug An example of the averaged
recirculation pattern inside a plug is shown in Fig 10afor Qaq=QIL=3534 mlhr It consists of two counter
rotating vortices with closed streamlines and symmetrical about the channel axis The recirculation
intensity within the plug is characterized by the recirculation time which is the time needed to displace
material from one to the other end of the plug (Thulasidas et al 1997 Kececi et al 2009 Dore et al
2012) A two-dimensional recirculation time was calculated as follows (Dore et al 2012)
τ(x) =Lpy0
int u(xy)dyy0
0
congLPy0
∆ sum ui|xi=Ni=1
(14)
where yo is the location of the stagnation point projected onto the observation mid-plane As can be seen
from Fig 10b the recirculation time is almost constant in the middle of the channel but increase towards
the front and back ends of the plug where the streamlines are not well defined The recirculation time is
usually treated as constant inside the liquid plug(Thulasidas et al 1997 Kashid et al 2005 Tsoligkas et
al 2007) However Dore et al (2012)experimentally found that the circulation pattern may not be fully
symmetric especially at shorter plugs
The recirculation times averaged for the middle part of the plug are plotted in Fig 11 against the plug
travel time in the 05mm ID channel for Qaq=QIL=3534 to 2121 mlhr The plug travel time is defined as
the time needed by the liquid plug to travel a distance of its own length given by Tp=LpUmix where Lp is
the plug length The corresponding mass transfer coefficients are also plotted As discussed above high
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
12
mixture velocities (Umix) result in shorter plug lengths thus leading to a shorter plug travel time (Tp) In
shorter plugs decreased recirculation times are observed which means the fluid in the plug will
experience a larger number of revolutions and better mixing This is supported by the increase in the
mass transfer coefficient at low Tp where the circulation time is also short A similar trend was also
observed by Kashid et al (2005)who argued that high mixture velocities increase recirculation intensity
because of increased shear between the wall surface and the plug Meanwhile higher mixture velocity
increases the thickness of the film surrounding the plug and decreases the plug diameter which results in
a shorter path length for the Eu(III) diffusion in the radial direction that also helps mass transfer
37 Comparison of KLa with correlations
Mass transfer in multiphase small scale units is a complex process which depends not only on the
hydrodynamic characteristics but also on the kinetics of the species transfer Several models have been
proposed to estimate mass transfer coefficients in gas-liquid and liquid-liquid plug flow either empirical
or developed from the film and penetration theories Bercic and Pintar (1997) suggested a correlation
Eqn(15) for gas-liquid flow which considers only the contribution of the plug caps since as the authors
argued the film becomes quickly saturated This model was able to predict accurately 119896119871120572for long
bubbles and liquid slugs Vandu et al (2005) suggested a model for the mass transfer coefficient where
the dominant contribution was from the film (Eqn 16) A constant was introduced whose value was
estimated from the best fitting of experimental data from different unit cell lengths LUC gas hold up εG
and rise velocity Up Yue et al (2009) proposed an empirical correlation (Eqn 17) suitable for short films
and non-uniform concentration in the plugs which differs from the well mixed assumption of the
previous models Similarly Kashid et al (2010) developed an empirical correlation (Eqn 18) specifically
for liquid-liquid plug flow as a function of Reynolds number Capillary number diameter and length of
the capillary The correlation was able to predict the experimental data within 95 even when the density
viscosity and interfacial tension of the aqueous phase was changed with the addition of surfactants
The mass transfer coefficients measured in 02 and 05mm ID channels are compared with these
correlations in Fig12The fitting parameters in the correlations byVandu et al (2005) (Eqn16) Yue et al
(2009)(Eqn 17) and Kashid et al (2010) (Eqn 18) were determined from least square regression analysis
of the data in both channels
119896119871120572 = 0111(119880119901+119880119904)
119
((1minus 119866)119871119880119862)057 (15 Bercic and Pintar 1997)
119896119871120572 = 365radic119863119880119901
119871119880119862
1
119868119863 (16 Vandu et al 2005)
119896119871119886 =167
119868119863(
119880119901
119868119863)
05
(119871119901
119868119863)
015
(119871119901+119871119878
119868119863)
005
(17 Yue et al 2009)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
13
119896119871120572119871119901
119906119898119894119909= 00257119862119886minus06119877119890005 (
119868119863
119871119901)
minus01
(18 Kashid et al 2010)
The model suggested by Bercic and Pintar (1997) shows deviations as high as 5541 compared to the
experiment results This correlation does not include the effect of channel size and it was developed for
velocities higher than those used in this work Besides the liquid slug length (3-135 cm) and unit cell
length (17-22 cm) considered for the model development were about 100 times larger than in the current
work The model byVandu et al (2005)gives better predictions particularly for the large channel with
standard deviation varying from 1153 to 4212 The correlation was in fact developed for gas-liquid
flow in 1-3 mm ID capillaries for bubbles and liquid slugs longer (LUC=5 ndash 60 mm) than in the present
work (LUC=0314-1153 mm) The predictions of the two empirical correlations (Eqn 17 and 18) are
better with deviations less than 20 The model by Yue et al (2009) (standard deviation 535-1672)
was developed based on the physical absorption of oxygen from rising air bubbles into water in square
microchannels with ID=04 mm The differences from the current data may be attributed to the low mass
transfer resistance in the gas phase bubbles compared to liquid plugs The model by Kashid et al (2010)
which was developed from liquid-liquid systems agrees best with the experiment results (standard
deviations 516 -1188) Empirical correlations may agree better with the experimental data because the
effects of chemical reaction kinetics and inlet junction configuration can be included in the constants
while such effects are not taken into account in the models based on film and penetration theory on a
fully formed plug (Eqn15 and Eqn16)
Preliminary Eu(III) extraction experiments were carried out with cyclohexane as organic phase diluent
for comparison in the 05 mm ID channel The Eu(III) was extracted with 50 TBP in cyclohexane from
2 M nitric acid and the distribution coefficient was found to be between 0024 and 0041 Under the same
flow rate of both phases the KLa of the cyclohexane system (00262-00643s-1) was similar to that of the
ionic liquid system (00339-00602s-1) However the Eu(III) initial loading when cyclohexane was used
was only 031 mgmL (2times10-3 M) because of the low limiting organic concentration (LOC) In
conventional systems like n-DD or cyclohexane as organic diluent the LOC of europium is 9 mgmL
beyond this concentration the organic phase will split into two phases a heavier (rich in metal-solvate)
and a lighter phase (rich in diluent) called third phase formation This is not observed when the ionic
liquid is used even when the loading of Eu(III) in the ionic liquid phase increased from 12 to 40 mgmL
(Rout et al 2011a) Therefore the high process capacity is an additional benefit of the present system
The mass transfer coefficients and interfacial areas found in this work are compared against those from
other microfluidic units and conventional extract ion units in Table 2 For the comparisons of KLa values
in microfluidic system previous studies using different liquid-liquid extraction systems are listed as well
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
14
As can be seen the interfacial areas are comparable to those obtained in other microfluidic systems but
significantly higher than those in conventional extraction units The mass transfer coefficients are again
higher than the ones achieved in conventional extractors but not as high as those in different microfluidic
applications This may be due to the low distribution coefficients found for the Eu(III) extraction
4 Conclusions
The intensified extraction of Eu from nitric acid solutions into an ionic liquid phase 02M CMPO-12M
TBP[C4mim][NTf2] was studied experimentally in small channels with diameters 02 and 05 mm
Experiments were carried out in the plug flow regime where the aqueous solution formed the dispersed
plugs and the ionic liquid solution was the continuous phase Phase equilibrium studies showed that the
distribution coefficients had the highest value at nitric acid concentration equal to 1M The geometric
characteristics of the flow pattern (plug length film thickness and interfacial area) were investigated with
high speed imaging while velocity fields within the aqueous phase plugs were obtained using high speed
bright field micro PIV
The results revealed that the interfacial areas and the mass transfer coefficients were significantly higher
than in conventional contactors In addition KLa were found to be higher in the small channel compared
to the large one for the same mixture velocities as a result of large interfacial areas and reduced
circulation times Within the same channel the mass transfer coefficients increased and then decreased
with increasing nitric acid concentration in accordance with the partition coefficients The mass transfer
coefficients were also found to decrease with residence time suggesting that significant mass transfer
occurs at the channel inlet The mixture velocity affected the mass transfer coefficient particularly in the
case of 1M nitric acid concentration The circulation times within the plugs calculated from the detailed
velocity profiles were found to decrease with decreasing plug size and increasing mixture velocity small
circulation times result in better mixing and mass transfer The empirical correlation suggested by Kashid
et al (2010) was able to predict the current results (with deviations 516-1188) better than other
literature correlations
Nomenclature
Latin Symbols
Ca Capillary number Ca=120583119868119871119880119898119894119909
120574 dimensionless
Caqini initial concentration of Eu(III) in aqueous phase molL-1
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
15
Caqfin final concentration of Eu(III) in aqueous phase molL-1
119862119886119902119890 Eu(III) concentration in aqueous phase at equilibrium molL-1
C(HNO3) nitric acid concentration M
CL channel length cm
D Eu(III) diffusion coefficient m2 s-1
DEu Eu(III) distribution coefficient
Eeff extraction efficiency
KL overall mass transfer coefficient ms-1
KLa overall volumetric mass transfer coefficient s-1
KLcap mass transfer via cap s-1
KLfilm mass transfer via film s-1
Lfilm film length m
119871119875 plug length m
Ls slug length m
119871119880119862 length of unit cell m
n Refractive index dimenionless
N mass transfer flux mol m-2s-1
Qaq volumetric flow rate of aqueous phase mlh-1
QIL volumetric flow rate of ionic liquid phase mlh-1
ID channel internal diameter mm
R channel internal radius mm
Re Reynolds number Re=
120588119880119898119894119909119868119863
120583 dimensionless
tfilm Contact ime of liquid film s
Umix mixture velocity cms-1
Up plug velocity cms-1
Ufilm film velocity cms-1
119882119901 plug width m
Greek Symbols
120572119901 plug interfacial area m2m-3
ρ density kgm-3
τ residence time s
δfilm film thickness mm
μ dynamic viscosity cp
γ Interfacial tension mNm-1
∆ dimensionless parameter
∆119871119872119862119863 log mean concentration difference molm-3
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
16
Acknowledgements
Financial support from the UCL Engineering Faculty and China Scholarship Council are gratefully
acknowledged The authors would like to thank Prof Kenneth R Seddon and Dr Natalia V Plechkova of
Queenrsquos University Ionic Liquids Laboratories (QUILL) for providing the ionic liquids and the UK
Engineering and Physical Sciences Research Council (EPSRC) for the loan of the Photron Ultima APX
high-speed camera
References
Alper E 1988 Effective interfacial area in the RTL extractor from rates of extraction with chemical reaction
Chemical engineering research amp design 66 147-151
Assmann N Ładosz A Rudolf von Rohr P 2013 Continuous Micro Liquid-Liquid Extraction Chemical
Engineering amp Technology 36 921-936
Bapat P Tavlarides L 1985 Mass transfer in a liquid-liquid CFSTR AIChE Journal 31 659-666
Bercic G Pintar A 1997 The role of gas bubbles and liquid slug lengths on mass transport in the Taylor
flow through capillaries Chemical Engineering Science 52 3709-3719
Billard I Ouadi A Gaillard C 2011a Liquidndashliquid extraction of actinides lanthanides and fission
products by use of ionic liquids from discovery to understanding Anal Bioanal Chem 400 1555-1566
Billard I Ouadi A Jobin E Champion J Gaillard C Georg S 2011b Understanding the Extraction
Mechanism in Ionic Liquids UO22+HNO3TBPC4-mimTf2N as a Case Study Solvent Extraction and Ion
Exchange 29 577-601
Binnemans K 2007 Lanthanides and actinides in ionic liquids Chemical reviews 107 2592-2614
Brigham DM 2013 Lanthanide-Polyaminopolycarboxylate Complexation Kinetics in High Lactate Media
Investigating the Aqueous Phase of TALSPEAK WASHINGTON STATE UNIVERSITY
Burns JR Ramshaw C 2001 The intensification of rapid reactions in multiphase systems using slug flow
in capillaries Lab Chip 1 10-15
Caldin E 2001 The mechanisms of fast reactions in solution IOS Press
Chinaud M Roumpea E-P Angeli P 2015 Studies of plug formation in microchannel liquidndashliquid flows
using advanced particle image velocimetry techniques Experimental Thermal and Fluid Science 69 99-110
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
17
Chun S Dzyuba SV Bartsch RA 2001 Influence of Structural Variation in Room-Temperature Ionic
Liquids on the Selectivity and Efficiency of Competitive Alkali Metal Salt Extraction by a Crown Ether Anal
Chem 73 3737-3741
De Morais C 2000 Recovery of europium and yttrium from color TV tubes 55 Congresso Anual
Associacao Brasileria de Metalurgia e Materiais Rio de Janeiro Brazil
Dehkordi AM 2001 Novel Type of Impinging Streams Contactor for LiquidminusLiquid Extraction Industrial
amp Engineering Chemistry Research 40 681-688
Dehkordi AM 2002 Liquid-liquid extraction with an interphase chemical reaction in an air-driven
two-impinging-streams reactors Effective interfacial area and overall mass-transfer coeffcient Ind
EngChem Res 41 4085-4093
Dessimoz A-L Cavin L Renken A Kiwi-Minsker L 2008 Liquidndashliquid two-phase flow patterns and
mass transfer characteristics in rectangular glass microreactors Chemical Engineering Science 63 4035-4044
Dore V Tsaoulidis D Angeli P 2012 Mixing patterns in water plugs during waterionic liquid segmented
flow in microchannels Chemical Engineering Science 80 334-341
Fernandes JB Sharma MM 1967 Effective interfacial area in agitated liquidmdashliquid contactors
Chemical Engineering Science 22 1267-1282
Ghaini A Kashid MN Agar DW 2010 Effective interfacial area for mass transfer in the liquidndashliquid
slug flow capillary microreactors Chemical Engineering and Processing Process Intensification 49 358-366
Goonan TG 2011 Rare Earth Elements--end Use and Recyclability US Department of the Interior US
Geological Survey
Horwitz EP Kalina DG Kaplan L Mason GW Diamond H 1982 Selected
Alkyl(phenyl)-NN-dialkylcarbamoylmethylphosphine Oxides as Extractants for Am(III) from Nitric Acid
Media Separation Science and Technology 17 1261-1279
Jovanović J Rebrov EV Nijhuis TA Kreutzer MT Hessel V Schouten JC 2012 LiquidndashLiquid
Flow in a Capillary Microreactor Hydrodynamic Flow Patterns and Extraction Performance Industrial amp
Engineering Chemistry Research 51 1015-1026
Kashid MN Gupta A Renken A Kiwi-Minsker L 2010 Numbering-up and mass transfer studies of
liquidndashliquid two-phase microstructured reactors Chemical Engineering Journal 158 233-240
Kashid MN IGerlach SGoetz JFranzke JFAcker FPlatte DWAgar STurek 2005 Internal
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
18
circulation within the liquid slugs of a liquidndashliquid slug-flow capillary microreactor IndustrialampEngineering
Chemistry Research 2005 5003-5010
Kashid MN Platte F Agar D Turek S 2007 Computational modelling of slug flow in a capillary
microreactor Journal of Computational and Applied Mathematics 203 487-497
Kececi S Woumlrner M Onea A Soyhan HS 2009 Recirculation time and liquid slug mass transfer in
co-current upward and downward Taylor flow Catalysis Today 147 S125-S131
Khakpay A Abolghasemi H Salimi-Khorshidi A 2009 The effects of a surfactant on mean drop size in a
mixer-settler extractor Chemical Engineering and Processing Process Intensification 48 1105-1111
Kiwi-Minsker L Renken A 2005 Microstructured reactors for catalytic reactions Catalysis Today 110
2-14
Kučera J Mizera J Řanda Z Vaacutevrovaacute M 2007 Pollution of agricultural crops with lanthanides thorium
and uranium studied by instrumental and radiochemical neutron activation analysis Journal of Radioanalytical
and Nuclear Chemistry 271 581-587
Lee C-J Yang B-R 1995 Extraction of trivalent europium via a supported liquid membrane containing
PC-88A as a mobile carrier The Chemical Engineering Journal and the Biochemical Engineering Journal 57
253-260
Lew K 2010 The 15 Lanthanides and the 15 Actinides The Rosen Publishing Group 30
Loumlwe H Ehrfeld W 1999 State-of-the-art in microreaction technology concepts manufacturing and
applications Electrochimica Acta 44 3679-3689
Matsumiya M Suda S Tsunashima K Sugiya M Kishioka S-y Matsuura H 2008 Electrochemical
behaviors of multivalent complexes in room temperature ionic liquids based on quaternary phosphonium
cations Journal of Electroanalytical Chemistry 622 129-135
Nakashima K Kubota F Maruyama T Goto M 2003 Ionic liquids as a novel solvent for lanthanide
extraction Analytical Sciences 19 1097-1098
Nakashima K Kubota F Maruyama T Goto M 2005 Feasibility of ionic liquids as alternative
separation media for industrial solvent extraction processes Industrial amp Engineering Chemistry Research 44
4368-4372
Okamura H Sakae H Kidani K Hirayama N Aoyagi N Saito T Shimojo K Naganawa H Imura
H 2012 Laser-induced fluorescence and infrared spectroscopic studies on the specific solvation of
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
19
tris(1-(2-thienyl)-444-trifluoro-13-butanedionato)europium(III) in an ionic liquid Polyhedron 31 748-753
Okubo Y Maki T Aoki N Hong Khoo T Ohmukai Y Mae K 2008 Liquidndashliquid extraction for
efficient synthesis and separation by utilizing micro spaces Chemical Engineering Science 63 4070-4077
Puranik S Sharma M 1970 Effective interfacial area in packed liquid extraction columns Chemical
Engineering Science 25 257-266
Rabah MA 2008 Recyclables recovery of europium and yttrium metals and some salts from spent
fluorescent lamps Waste management 28 318-325
Raimondi NDM Prat L Gourdon C Tasselli J 2014 Experiments of mass transfer with liquidndashliquid
slug flow in square microchannels Chemical Engineering Science 105 169-178
Rao CJ Venkatesan K Nagarajan K Srinivasan T Rao PV 2009 Electrochemical behavior of
europium (III) in N-butyl-N-methylpyrrolidinium bis (trifluoromethylsulfonyl) imide Electrochimica Acta 54
4718-4725
Resende LV Morais CA 2010 Study of the recovery of rare earth elements from computer monitor scraps
ndash Leaching experiments Minerals Engineering 23 277-280
Ribeiro A Valente A Lobo V 2011 Diffusion behaviour of trivalent metal ions in aqueous solutions
Chemistry and Chemical Technology 5
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011a Extraction and third phase formation
behavior of Eu(III) IN CMPOndashTBP extractants present in room temperature ionic liquid Separation and
Purification Technology 76 238-243
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2011b Room temperature ionic liquid
diluent for the extraction of Eu(III) using TRUEX extractants Journal of Radioanalytical and Nuclear
Chemistry 290 215-219
Rout A Venkatesan KA Srinivasan TG Vasudeva Rao PR 2012 Extraction behavior of actinides and
fission products in amide functionalized ionic liquid Separation and Purification Technology 97 164-171
Sarkar S Mumford CJ Phillips CR 1980 Liquid-Liquid Extraction with Interphase Chemical Reaction
in Agitated Columns 1 Mathematical Models Industrial amp Engineering Chemistry Process Design and
Development 19 665-671
Scheiff F Mendorf M Agar D Reis N Mackley M 2011 The separation of immiscible liquid slugs
within plastic microchannels using a metallic hydrophilic sidestream Lab Chip 11 1022-1029
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
20
Schulz W Horwitz E 1986 Recent progress in the extraction chemistry of actinide ions Journal of the Less
Common Metals 122 125-138
Sen N Darekar M Singh K Mukhopadhyay S Shenoy K Ghosh S 2014 Solvent extraction and
stripping studies in microchannels with TBP nitric acid system Solvent Extraction and Ion Exchange 32
281-300
Sengupta A Mohapatra PK Iqbal M Verboom W Huskens J Godbole SV 2012 Extraction of
Am(iii) using novel solvent systems containing a tripodal diglycolamide ligand in room temperature ionic
liquids a lsquogreenrsquo approach for radioactive waste processing RSC Advances 2 7492
Sukhamoy Sarkar JMumford C RPhillips C 1980 Liquid-liquid extraction with an interphase chemical
reaction in agitated columns1 Mathmatical models Industrialamp Engineering Chemistry Process Design and
Development 19 665-671
Thulasidas T Abraham M Cerro R 1997 Flow patterns in liquid slugs during bubble-train flow inside
capillaries Chemical Engineering Science 52 2947-2962
Tsaoulidis D Angeli P 2015 Effect of channel size on liquid-liquid plug flow in small channels AIChE
Journal na-na
Tsaoulidis D Dore V Angeli P Plechkova NV Seddon KR 2013 Dioxouranium(VI) extraction in
microchannels using ionic liquids Chemical Engineering Journal 227 151-157
Tsoligkas AN Simmons MJH Wood J 2007 Influence of orientation upon the hydrodynamics of gasndash
liquid flow for square channels in monolith supports Chemical Engineering Science 62 4365-4378
Vandu CO Liu H Krishna R 2005 Mass transfer from Taylor bubbles rising in single capillaries
Chemical Engineering Science 60 6430-6437
Verma R Sharma M 1975 Mass transfer in packed liquidmdashliquid extraction columns Chemical
Engineering Science 30 279-292
Wang G Peng Q Li Y 2011 Lanthanide-doped nanocrystals synthesis optical-magnetic properties and
applications Accounts of chemical research 44 322-332
Kashid MN Harshe YM Agar DW2007 Liquid-liquid slug flow in capillary an alternative to suspended
drop or film contactors Industrial ampEngineering Chemistry Research 46 8420-8430
Kashid MN Renken A Kiwi-Minsker L 2011 Influence of flow regime on mass transfer in different
types of microchannels Industrial ampEngineering Chemistry Research 50 6906-6914
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
21
Xu B Cai W Liu X Zhang X 2013 Mass transfer behavior of liquidndashliquid slug flow in circular
cross-section microchannel Chemical Engineering Research and Design 91 1203-1211
Yang L Zhao Y Su Y Chen G 2013 An Experimental Study of Copper Extraction Characteristics in a
T-Junction Microchannel Chemical Engineering amp Technology 36 985-992
Yang X He L Qin S Tao G-H Huang M Lv Y 2014 Electrochemical and Thermodynamic
Properties of Ln(III) (Ln = Eu Sm Dy Nd) in 1-Butyl-3-Methylimidazolium Bromide Ionic Liquid PLoS
ONE 9 e95832
Yue J Luo L Gonthier Y Chen G Yuan Q 2009 An experimental study of airndashwater Taylor flow and
mass transfer inside square microchannels Chemical Engineering Science 64 3697-3708
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
22
Tables
Table 1
Properties of the test fluids
Propertyparameter (25ordmC) Fluidvalue
Density (ρ)[kgm3] Ionic liquid phase 1259
Aqueous phase 1030
Dynamic viscosity (μ)[cp] Ionic liquid phase 2559
Aqueous phase 075
Interfacial tension(γ)[mNm] Ionic liquid phase Aqueous phase =670
Eu(III) diffusion coefficient(D)[ m2 s-1] Ionic liquid phase 295times 10-12
Aqueous phase 786 times 10-8
Refractive index(n) Ionic liquid phase 1427
Aqueous phase 1339
FEP channel 134
Deionized water 1335
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
23
Table 2
Comparison of KLa values in liquid-liquid microfluidic systems using TY-junctions
Liquid-liquid
contactor
System KLa (s-1) α (m2 m-3) Reference
T-junction capillaries
ID=02 and 05mm
02M CMPO-12M
TBP[C4mim][NTf2]---1M
nitric acid
0005-005 3750-8250 Present work
T-junction capillaries
ID= 05mm
50 TBP in cyclohexane---1M
nitric acid
00262-00643 3613-3979 Present work
Soda-lime glass
038mm depth chip
Keroseneacetic acid
water+NaOH
Order of
magnitude of
05
NA Burns and
Ramshaw
(2001)
PTFE capillary with
Y-junction 05 075
and 1mm
Kerosenen-butanolwater 002-031 590-4800 Kashid et
al(2007)
Rectangular glass
microchannel 04mm
Hexane trichloroacetic acid
water+NaOH
02-05 10700-112
00
Dessimoz et
al (2008)
Capillary microreactor
ID=05mm
n-butyl formate-aqueous
NaOH solution
090-167 1600-3200 Ghaini et al
(2010)
Square (glass 04mm)
T-square (glass
04mm) T-trapezoidal
0269mm)
Y-rectangular (015mm
ID) Concentric (glass
015mm)
Nonreacting water-acetone ndash
toluene
001-074 NA Kashid et al
(2011)
Opposed T-junction
ID=06 08 and 10mm
Sodium hydroxide---n-butyl
acetate
0006-037 1300-4100 Xu et al
(2013)
T-junction Teflon
channel ID=05mm
30TBP in
[C4mim][NTf2]---3M nitric
acid
0049-0312 NA Tsaoulidis et
al (2013)
T-junction PTFE
capillary with 2mm ID
00016 to 045ms
CuSO4H2SO4AD-100260 003-026 NA Yang et al
(2013)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
24
T-junction serpentine
microchannel
ID=0278 and 0319
mm
30 TBP in dodecane (nitric
acid)--- water
0001-4 NA Sen et al
(2014)
Square Glass
T-junction
microchannel 210 μm
Wateracetonetoluene 161-844
6090-1340
0
Raimondi et
al (2014)
Packed extraction
columns
n-butyl formate-aqueous
NaOH solution
00034-0005 80-450 Verma and
Sharma
(1975)
RTL extractors
(Graesser raining
bucket)
n-butyl formate-aqueous
NaOH solution
(06-13)times10-6 90-140 Alper (1988)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
25
Fig1 Sketch of the experimental set up including the high speed imaging system
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
26
Fig 2Top view sketch of the 02mm ID microchip
Fig 3 Chemical structure of the ionic liquid 1-butyl-3-methylimidazolium
bis[(trifluoromethyl)sulfonyl]amide ([C4min][NTf2])
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
27
Fig 4 Specific interfacial area against mixture velocity for different capillary diameters
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2]
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
28
Fig 5 Eu(III) distribution coefficients against initial nitric acid concentration at different initial Eu(III)
loading Aqueous phase 001-2M HNO3 organic phase 02M CMPO-12M TBP[C4mim][NTf2]
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
29
(a)Volumetric mass transfer coefficients
(b) Extraction efficiency
Fig 6 Variation of Eu(III) (a) extraction efficiency and (b) volumetric mass transfer coefficient with
residence time for different initial nitric acid concentrations Umix=05cms CL=5 15 25cm
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
30
Fig 7 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different initial
nitric acid concentrations CL=15cm 05mm ID
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
31
Fig 8 Variation of Eu(III) extraction efficiency with residence time for different initial nitric acid
concentrations CL=15cm 05mm ID
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
32
Fig 9 Variation of Eu(III) volumetric mass transfer coefficient with mixture velocity for different
capillary sizes 02mm and 05mm ID CL=25cm
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
33
(a) Averaged recirculation pattern
(b) Averaged recirculation time
Fig10 (a) Averaged recirculation pattern and (b) averaged recirculation time profile along an aqueous
plug 05mm ID channel Qaq=QIL=3534mlh
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)
34
Fig 11 Recirculation time and mass transfer coefficient as a function of plug travel time
Aqueous phase 1M nitric acid organic phase 02M CMPO-12M TBP[C4mim][NTf2] CL=15cm
05mm ID Qaq=QIL
35
Fig 12 Comparison of experimental KLa values against predicted ones
(System 1M nitric acid-02M CMPO-12M TBP[C4mim][NTf2] Qaq=QIL ID=02 and 05 mm capillary)